The science

The cited findings behind Anglrithm's guidance: what each study measured, where it was done, how we read it, and a link to the source. Guidance sits beside the score, never in it, and an entry we have read only in its abstract shows no numbers until its full text is read.

The library

484 entries. 161 show their findings here: 83 read in full text, 64 agency documents, 17 of them re-read in full against their source. The other 323 were read only in their abstract; they are listed at the end by citation, abstract read, numbers withheld.

In thirteen years of angler-level data, the things the angler chose (bait, technique, whether a guide was aboard) had larger effects than any environmental variable measured. Conditions are the smaller half of this.

Library built Oct 16, 2026. Each entry is paraphrased in our own words with its DOI or agency link.

What the evidence does not say

  • The pressure studies here are about storms moving fish, not about catch: tagged fish left reefs and nurseries as pressure fell ahead of storms. Barometric pressure stays labelled not supported in the score.
  • Cyclonic eddies held more Sargassum than eddy-free water; that study measured weed, not mahi.
  • In Gulf longline data, satellite temperature breaks alone did not show where yellowfin were caught (Power & May 1991), and yellowfin catches showed little link to eddies or surface temperature (Teo 2010).
  • Moon phase does not decide the bite: the studies cited find its effect on catch inconsistent or absent (Hanson 2008; Debaere 2024), and the score counts the moon at half weight where it counts it at all.
  • The research programs named on this page are cited, not endorsed.
Solunar tablesPopular belief, not supported

The best-powered test of solunar tables found nothing. One angler, 361 trips and 1,355 hours, seven commercial solunar services, corrected for multiple testing, with 99 percent power to detect a medium effect: no relationship between any solunar value and catch rate. Just two results were significant, and both were negative, with trips inside predicted minor windows yielding 42.5 percent fewer fish per hour. Air temperature beat every solunar prediction.

Quigley, Gonzalez Murcia & Kauwe 2023, SN Applied Sciences 5:162.

Barometric pressure trendPopular belief, not supported

A 30 hPa swing, which is about the biggest front of the year, is the same pressure change a fish feels by swimming down a foot. The direct feeding experiment on yellow perch found no significant influence, and thirteen years of angler data did not surface pressure trend as a meaningful predictor. It is also unidentifiable in principle from a catch log, because the barometer moves with the wind, the cloud and the temperature.

VanderWeyst 2013, Bemidji State University. Shaw et al. 2021, PLOS ONE 16:e0257882.

Both stay in the score, discounted to a fifth of their weight and captioned, and neither is promoted.

The findings

Water temperature

  • The January 2010 freeze cut tagged snook survival by over 90 percent on SW Florida barrier islands.

    Water fell from about 18 C to 12 C within 5 days in January 2010 and stayed below 12 C to 16 January; at least 10 days below the 12.5 C snook lethal level. Apparent survival of marked snook fell 96-97 percent; 2010 abundance was 76 and 42 percent below 2008 and 2009.

    SW Florida Gulf barrier islands · field · full text read

    Adams et al. 2012
  • A water temperature anomaly typically fades over about two to three weeks, faster in summer.

    From 37 years of daily satellite SST, median short-term anomaly persistence (lag where a fitted exponential falls to correlation 0.6, about 61 percent of e-folding time) was 11 to 14 days over 71 to 79 percent of the ocean: 11 days for June starts, 14 for March. Persistence is shorter in summer and in eddy-rich regions.

    Global ocean (satellite, 1981-2018) (outside South Florida) · field · full text read

    Bulgin et al. 2020
  • Adding a model's forecast anomaly to the observed normal removes model bias and gave useful skill about 2 months out.

    Forecast SST anomalies were formed by subtracting the model's own 1982-2010 climatology for the same start date and lead, then added to the observed climatology to get absolute temperatures for a tag-based tuna habitat model. Expected useful habitat forecast skill was up to 2 months; daily-updated forecasts were adopted by the purse-seine industry.

    Great Australian Bight (out of region) (outside South Florida) · model · full text read

    Eveson et al. 2015
  • Panhandle kingfish catch rates tended to drop after very cold winters and rise after warm ones.

    Panama City charter logs 1970-1979 (22,349 fish, 60.8% king mackerel). Catch per hour was 3.8 in 1975 after a warm winter, but 1.4 in 1977 and 1.3 in 1978 after winters averaging 8.6 and 8.9 C air temperature. Catches peaked August-September. Authors called the data too few to be conclusive; air temperature proxy.

    Florida Panhandle (Panama City) · field · full text read

    Fable et al. 1981
  • Tiger sharks favor water near 27-28 C, and in warm years they push farther north and arrive earlier.

    47 SPOT-tracked sharks 2010-2019 plus 8,764 captures 1980-2018. Presence peaked at SST 27-28 C; captures were highest at 22-28 C. Each 1 C warm anomaly moved arrival north of 36N about 14 days earlier. High-catch areas shifted 300-440 km poleward over decades. Mostly females tagged off Florida and the Bahamas.

    SE Florida; western North Atlantic · field · full text read

    Hammerschlag et al. 2022
  • NOAA's pass mark for a coastal forecast model is 90 percent of temperature errors within 3 C.

    NOS standards require 90 percent of errors within an acceptable error X and under 1 percent beyond 2X. X is 15 cm for water level, 26 cm/s current speed, 3.0 C water temperature and 3.5 psu salinity, as used for TBOFS and NGOFS2; temperature and salinity X derive from ship draft density error. Ideal assessment uses 365 days.

    U.S. coastal (NOAA standard); Tampa Bay and northern Gulf OFS · agency · agency document

    Hess et al. 2003
  • Adult lemon sharks gather off southeast Florida each winter when water drops below about 24 C, then disperse north.

    83 adult lemon sharks tracked 2007-2011: 97.5% of detections fell in a December-April residency when local water stayed below about 24 C. Water temperature was the strongest predictor; moon phase had no effect. Highest residence was at artificial reefs on the 20-30 m reef line. In summer sharks ranged north to Cape Hatteras.

    SE Florida · field · full text read

    Kessel et al. 2014
  • Mahi, wahoo and yellowfin patches match surface temperature patches, but swordfish patches match temperature at 200 m.

    U.S. Gulf longline logbooks (1987-2005, about 3,389 sets per year) gave average patch scales of 54.9 km for dolphinfish, 54.3 km wahoo, 92.2 km yellowfin and 133.3 km swordfish. SST patches averaged 72.4 km and 200 m temperature 143.3 km. Surface species tracked the SST scale; swordfish tracked the 200 m scale. Longline gear only.

    Gulf of Mexico (outside South Florida) · field · full text read

    Kleisner et al. 2010
  • Florida pompano die when water drops to about 10 to 12 C, and grow best at 25 to 30 C.

    Aquaculture species profile: mortalities occur at 10-12 C and with sudden large temperature changes; juveniles grow best at 25-30 C and have thrived up to 34 C. Juveniles and adults tolerate 0-50 ppt salinity and dissolved oxygen of 4 mg/L or more.

    Florida (Mote Marine Lab culture profile) · agency · agency document

    Main et al. 2007
  • Blacktips here tracked shallow seagrass and water above 31 C; salinity and oxygen were not top drivers.

    BRT models of 245 blacktips (2013-2018): depth 54.4 percent, temperature 13.4 percent and bottom type 8.2 percent were top predictors; preferred under 4 m, over 31 C, seagrass. Salinity (about 24-36 PSU) and DO (4.6-8.0 mg/L) were tested but not among top three.

    West-central Florida (Pinellas), just north of box · model · full text read

    Mullins et al. 2021
  • The 2010 freeze hit snook, tarpon and ladyfish hardest in Everglades waters; redfish survived better.

    NPS reported in January 2010 that snook, tarpon, ladyfish, catfish, pinfish and mojarra were hardest hit across western rivers, Whitewater Bay and Florida Bay; thousands of large dead snook, tarpon and goliath grouper at Flamingo. Red drum and black drum reportedly fared better. No water temperatures given.

    Everglades National Park, Florida Bay, Flamingo · agency · agency document

    National Park Service, Everglades National Park 2010
  • White marlin catch rates climb as surface water warms to about 25 C, then level off.

    Mexican observer data, 79,642 longline sets 1993-2023, white marlin in 18% of sets. Delta GAMM: catch rose with SST to around 25 C then flattened, was higher late in the year and toward the open central Gulf. Squid and octopus bait beat fish bait. Models explained only 11.2-12.5% of variation.

    southwestern Gulf of Mexico, Mexican waters (out of region) (outside South Florida) · agency · agency document

    Ramirez-Lopez et al. 2025
  • Juvenile lemon sharks hug Cape Canaveral beaches in winter, flee south when water drops near 12 C, and head north as spring warms.

    54 tagged juveniles (2008-2011, 300 km array) wintered in the Canaveral surf zone, 82% of detections nearshore; over 70% were at 15-20 C. In the January 2010 cold event water fell to 11 C and all left, moving 62-191 km south to water 3-6 C warmer. Northward spring passage ran late February to early May.

    east-central Florida (Cape Canaveral to Palm Beach) · field · full text read

    Reyier et al. 2014
  • In January 2010 Sanibel's Tarpon Bay lost ladyfish, tarpon, mullet and gag to cold.

    SCCF monitoring summary of the January 2010 event: record-low water temperatures since its sensors began in 2007; fish kill species in Tarpon Bay included ladyfish, tarpon, pinfish, filefish, mojarra, gag, mullet and catfish; snook mortality statewide, with abundance at least 49 percent below pre-event for four years.

    Sanibel, Tarpon Bay, SW Florida · field · agency document

    Sanibel-Captiva Conservation Foundation Marine Laboratory 2010
  • In Florida Bay, tagged seatrout spent more time where water stayed below 30 C, and fed most around dawn.

    Preliminary FIU telemetry (75 tagged seatrout, 29 receivers, 16 temperature loggers) in Rankin Basin: fish spent more time in areas below 30 C; dawn (about 6-7 AM) appeared to be peak feeding. Near 30 C in the dry and early wet season, higher metabolic cost may limit feeding. Results unpublished at time of report.

    Rankin Basin, north-central Florida Bay · agency · agency document

    SECOORA
  • Around reefs, amberjack hold in the warm mixed layer; offshore they dive deep but body temperature limits how long they stay down.

    Archival and satellite tags on 12 amberjack (68-101 cm FL, 1,331 tag-days). Near reefs fish stayed mostly in 20-22 C mixed water with short dives; offshore they made daily dives to 150-250 m. Body temperature lagged water temperature and rarely fell below 16 C; 95% of dives lasted under 21 minutes. Taiwan, not Florida.

    Taiwan, East China Sea (out of region) (outside South Florida) · field · full text read

    Tone et al. 2022
  • After a severe Florida cold kill, gray snapper growth stalled for a year then ran faster, and snook switched sex younger.

    Otolith increments from fishery-caught gray snapper showed growth fell 46% the year after a severe cold event versus a pre-event control, then ran 16-17% above control for several years. In a northern estuary where snook fell over 50%, snook became female younger and smaller. Interpreted as compensatory recovery; correlative design.

    Florida (statewide estuaries and fisheries) · field · full text re-read Oct 16, 2026

    Trotter et al. 2025
  • Short sensor gaps can be filled by interpolation, but not across a cold front.

    For a 2012-2022 air and water temperature dataset, gaps up to 3 h (air) and 5 h (water) were linearly interpolated only when values on each side differed by under 1.5 C; longer gaps used nearby stations. Test gaps of 6 to 168 h gave water temperature MAE 0.88 C; final data had under 2 percent gaps.

    Upper Laguna Madre, Texas (outside South Florida) · field · full text read

    White et al. 2024

Season

  • Gray snapper use inland mangroves in the dry season and shift to Keys mangroves in the wet season.

    Visual surveys over more than 500 km of mangrove shoreline (2000-2001): mean salinity rises and variability falls toward Keys inlets. Gray snapper selected inland mainland mangroves in the dry season (December-February) and Keys shorelines in the wet season (June-August); other snappers and grunts favored Keys mangroves year round.

    Biscayne Bay to NE Florida Bay and Upper Keys · field · full text read

    Faunce & Serafy 2008
  • Along Florida's Gulf coast, cobia and many sharks move north in spring and south in fall; tarpon head north later, in summer.

    Acoustic detections of 889 fish from 29 species, 2016 to 2018. Northbound moves dominated spring and southbound moves fall. Cobia, bull sharks and coastal sharks moved north more in spring; tarpon, cobia and bull sharks moved south more in fall. Tarpon northbound movement peaked in summer. Tampa Bay predator detections peaked in fall with red drum aggregations.

    Florida Gulf coast · field · full text read

    Friess et al. 2021
  • Great hammerheads return to the Jupiter area most years, mainly October through March, and leave as water warms.

    Acoustic, satellite and photo-ID work on great hammerheads (2000-2016; 31 acoustic tags) found seasonal residency off Jupiter Inlet from October to March, with some fish returning four seasons in a row. Residency fell as water temperature rose. Fish made return migrations up to 3030 km and some stayed up to 5 months.

    SE Florida; Bahamas (outside South Florida) · field · full text read

    Guttridge et al. 2017
  • Big migratory tarpon arrive in South Florida in late April and leave by late June, with a smaller fall push.

    Tag-recapture, creel data and satellite tags (10 tarpon, 16 bull sharks): adult tarpon over 45.4 kg were nearly absent December-March, arrived mid-late April and left by late June, with a smaller October-November surge. Bull shark catch peaked December-January. Tarpon crossed shark-dense deep water fast and spent over 90% of time moving slowly near shallow structure.

    Florida Keys; Florida Bay; Everglades; SW Florida · field · full text read

    Hammerschlag et al. 2012
  • Adult male tiger sharks winter around Bahamas-area islands and head to open Atlantic water north of Bermuda each summer.

    24 tiger sharks tagged at Bermuda, tracked up to 1,101 days. Sixteen larger sharks made yearly round trips over 7,500 km, wintering at Bahamas, Turks and Caicos or Anguilla, summering offshore, and staying in about 24-26 C water both seasons. The five smallest stayed near Bermuda. Few females were tracked.

    western North Atlantic, Bermuda and Bahamas (out of region) (outside South Florida) · field · full text read

    Lea et al. 2015
  • Most Florida-tagged dolphinfish are recaptured off Florida within about a week; others reach the Carolinas in about a month.

    Dolphinfish Research Program to SAFMC (2002-Aug 2020): 28,209 tags, 706 recoveries; 43% tagged and recaptured off east Florida (mean 6.8 days at liberty, 0-57). Florida to NC mean 32.6 days (n=73). Florida captains report later seasons, best months now August-September; tagging shifted from May toward June-August after 2012.

    East Florida to Mid-Atlantic; Bahamas; Caribbean (outside South Florida) · agency · agency document

    Merten 2020
  • Young swordfish center near the Caribbean in winter, move up the U.S. East Coast in spring and summer, and retreat south in fall.

    Pooled pop-up tags (38 of 78 deployments, Newfoundland to the Straits of Florida) showed tagged fish stayed in the western Atlantic. Immature fish (under 179 cm) centered in the Caribbean in January-March, shifted to the coast from south Florida to Cape Cod in April-June, went farther north in summer and retreated south in fall. Mature fish ranged farther north.

    western North Atlantic · field · full text read

    Neilson et al. 2014
  • Per ocean boat trip, east Florida dolphin catch peaks May-June; wahoo and blackfin peak September-December.

    MRIP 2021-2024, private plus charter ocean trips; catch per 1,000 trips indexed to max by wave (Jan-Feb to Nov-Dec): dolphin 0.16, 0.30, 1.00, 0.68, 0.80, 0.15; king mackerel 0.29, 0.68, 1.00, 0.75, 0.62, 0.57; wahoo 0.33, 0.37, 0.43, 0.10, 0.87, 1.00; blackfin 0.61, 0.89, 0.49, 0.36, 0.80, 1.00; cobia 0.81, 0.69, 0.45, 0.49, 0.90, 1.00.

    Florida Atlantic coast (MRIP South Atlantic Florida, excludes Monroe County) · agency · agency document

    NOAA Fisheries Marine Recreational Information Program 2025
  • Per trip, east Florida yellowtail peak September-October, gray snapper late summer, and mutton in winter.

    MRIP 2021-2024, private plus charter ocean trips; total catch per 1,000 trips indexed to max by wave (Jan-Feb to Nov-Dec): yellowtail 0.40, 0.55, 0.36, 0.45, 1.00, 0.57; mutton 1.00, 0.45, 0.52, 0.42, 0.64, 0.89; gray snapper 0.33, 0.58, 0.77, 0.89, 1.00, 0.73; amberjack 0.46, 0.99, 0.93, 1.00, 0.24, 0.51; red grouper 1.00, 0.55, 0.47, 0.36, 0.45, 0.48.

    Florida Atlantic coast (MRIP South Atlantic Florida, excludes Monroe County) · agency · agency document

    NOAA Fisheries Marine Recreational Information Program 2025
  • In Florida's Gulf plus Keys domain, dolphin catch per trip peaks July-August and blackfin and wahoo peak September-October.

    MRIP 2021-2024 private plus charter ocean trips; catch per 1,000 trips indexed to max (Jan-Feb to Nov-Dec): dolphin 0.02, 0.13, 0.56, 1.00, 0.46, 0.04; blackfin 0.27, 0.69, 0.24, 0.34, 1.00, 0.20; mutton 1.00, 0.21, 0.13, 0.11, 0.20, 0.48; yellowtail 1.00, 0.57, 0.44, 0.38, 0.46, 0.68; hogfish 1.00, 0.28, 0.17, 0.15, 0.32, 0.73.

    Florida Gulf coast including Monroe County (Keys) as one MRIP domain · agency · agency document

    NOAA Fisheries Marine Recreational Information Program 2025
  • Daily normals should be a smooth curve fitted with about six annual harmonics, not raw calendar-day averages.

    NCEI computes daily max and min temperature normals by a least squares fit of 6 harmonics (M=6) to raw day-of-year means, constrained so each month's daily normals average to the monthly normal; days with under 10 valid values borrow a wider window. Daily standard deviations use a 15-day window then a 29-day running mean.

    United States (method) · agency · agency document

    NOAA National Centers for Environmental Information 2021
  • A day-of-year normal from 10 to 23 years of data is usable but provisional; 24 of 30 years counts as standard.

    NCEI 1991-2020 normals are standard with at least 24 years (80 percent) of a 30-year period, representative with at least 10 years, and estimated from neighbours with at least 2 full years. Daily percentiles and frequencies pool all values in a 29-day window centered on each day, smoothed by a 29-day running mean, and require at least 10 qualifying years.

    United States (method) · agency · agency document

    NOAA National Centers for Environmental Information 2021
  • Cobia tagged in central and south Florida are detected in every month, with resident and migratory groups.

    SEDAR 58 stock ID review: acoustic tags in central and south Florida detected every month across 1,800 km; a resident group in central/south Florida and a migratory Keys/Gulf group, little exchange with Georgia-South Carolina. Virginia fish showed no December-March detections and wintered offshore; one PSAT popped off Daytona in February.

    Central and South Florida Atlantic coast; Keys/Gulf · agency · agency document

    Perkinson M , SEDAR 58 Stock ID spatial distribution and movement work group 2018
  • Spotted seatrout in Florida Bay spawn March through October, peaking June to September, mostly at 26-34 C water.

    Ichthyoplankton surveys 1994-1999 at up to 17 stations: seatrout larvae present March-October, peaks in June, August and September, absent in winter months. Most spawning occurred at 26-34 C (coldest catch 20 C) and 25-40 psu; larvae were rare or absent in the eastern and Atlantic transition zones and common in central and western basins.

    Florida Bay · field · full text read

    Powell 2003
  • Gulf blue marlin summer in U.S. Gulf waters and winter off Mexico; some pass through the Florida Straits toward Cuba and the Bahamas.

    Tags on 296 billfish, tunas and sharks (2003-2018, 22,289 daily positions) showed 59 blue marlin had 61.6% of July-September positions in the U.S. Gulf but over 70% of fall and winter positions off Mexico, some exiting via the Florida Straits. Yellowfin stayed mostly in the U.S. Gulf (89.5% of positions). Tiger sharks showed long U.S. residency.

    Gulf of Mexico and Florida Straits (outside South Florida) · field · full text read

    Rooker et al. 2019
  • Keys kingfish peak in winter as Gulf-group fish arrive; SE Florida holds some kingfish year-round.

    12,493 king mackerel tagged 1975-1979. Fort Pierce and Keys releases showed annual cycles: through SE Florida and Keys late winter to early spring, northern Gulf spring-summer, back by late summer-fall. Jupiter recaptures in SE Florida came in all months, suggesting residents. Keys returns peaked February-March. Stock overlap off SE Florida 29.4-41.8%.

    SE Florida (Jupiter, Fort Pierce) and Florida Keys · field · full text read

    Sutter FC et al. 1991
  • A month with 11 or more missing days, or 5 consecutive missing days, should not enter the normal.

    WMO-No. 1203 guidance as applied by NOAA and MET Norway: a normal needs data for at least 80 percent of years (24 of 30) with no more than 3 consecutive missing years. The WMO monthly rule implemented in xclim treats a month as missing when 11 or more days, or a run of 5 or more consecutive days, are missing.

    Global (WMO standard) (outside South Florida) · agency · agency document

    World Meteorological Organization 2017

Spawning

  • Everglades river snook vary more from year to year in leaving for spawning, likely tied to freshwater flow.

    Acoustic tracking of snook in the Shark River compared with a published Caloosahatchee study. Similar shares of fish stayed in the river through spawning season (presumed skipped spawning), but Shark River fish varied more between years, likely with freshwater flow and floodplain flooding, spent less time outside the river, and more left without returning.

    Everglades; Charlotte Harbor · field · full text re-read Oct 16, 2026

    Boucek et al. 2019
  • In September, red snapper, lane snapper and king mackerel eggs are common on the West Florida Shelf, sorted mainly by water depth.

    DNA barcoding of 4,833 fish eggs from September surveys in 2013, 2014 and 2019 identified 82 species. Water depth structured egg assemblages more than region. Red, lane and vermilion snapper, yellowedge grouper and king mackerel eggs were frequent. Back-tracking 36 hours put spawning 1 to 79 km away, mean about 21 km.

    West Florida Shelf · field · full text re-read Oct 16, 2026

    Keel et al. 2025
  • Cubera snapper aggregate to spawn in the Lower Keys in summer, on 26-35 m reef and on deep wrecks.

    Fisher-identified cubera spawning: reef at 26-35 m peaking June-August, and high-relief wrecks at 67-85 m in May and June. Text notes a deep wreck at 45-80 m fished for spawning cubera.

    Lower Florida Keys · survey · full text read

    Lindeman et al. 2000
  • Lower Keys snapper spawning runs mutton May-June, then cubera and gray snapper July-August, mostly on 12-37 m reef.

    Commercial fishers identified 22 potential snapper spawning sites in the Lower Keys. Peak months and site depths: mutton May-Jun at 12-37 m (one sand site 4-6 m); gray snapper Jul-Aug, July at some sites, at 9-37 m; yellowtail May-Jun at 26-30 m; lane snapper Jun at 17 m.

    Lower Florida Keys · survey · full text read

    Lindeman et al. 2000
  • Mutton snapper in Florida spawn mainly April through July, peaking May-June in the Keys around the full moon.

    FWC/UF gonad data: active spawners first in April, last in September; core season April-July; peak share of spawning-capable females about 60% in May-June in the Keys, under 10% in SE Florida, suggesting migration from SE Florida to Keys spawning grounds. Aggregations reported near full moon March-July.

    Florida Keys; SE Florida · agency · agency document

    Lowerre-Barbieri & Friess 2023
  • Seatrout spawn on evenings near the full moon, commuting from the bay and back within a day.

    32 tagged seatrout and passive acoustics at a Tampa Bay spawning inlet, 2005. 23 fish returned to spawn; most came from the estuary and went back within 24 hours. 82% of chorus hours fell 18:00 to midnight. Spawning odds rose near full moon; current had no effect. A red tide cut the season after 13 July.

    Tampa Bay · field · full text read

    Lowerre-Barbieri et al. 2013
  • Snook numbers at an inlet spawning site peak in June and July and around new and full moons.

    Capture sampling plus acoustic telemetry of 31 snook at a Tampa Bay inlet spawning site (2007-2009): fish numbers rose in June-July (peak spawning) and on new and full lunar phases. Snook showed annual and within-season fidelity to the site, with contingents using different overwintering habitats.

    Tampa Bay area, W Florida · field · full text re-read Oct 16, 2026

    Lowerre-Barbieri et al. 2014
  • Female gag stack up in shallow water in early winter before moving deep to spawn February to mid-April; males are scarce.

    Three-year study of 1,657 gag in the eastern Gulf. Spawning ran 1 February to 18 April. All-female pre-spawning groups formed on shallow sites (5 to 15 m) from November to February, while actively spawning females were taken at 65 to 99 m. Males were 5 percent of spawning-season catch in a protected area versus 15 percent expected, effectively zero elsewhere.

    eastern Gulf of Mexico (West Florida Shelf) (outside South Florida) · field · full text read

    Lowerre-Barbieri et al. 2020
  • Goliath grouper on summer and fall aggregation wrecks are most vocal after midnight and go quieter for several days around the full moon.

    Passive acoustic recorders on two SW Florida Gulf aggregation wrecks (about 25 and 40 fish) logged low 60 Hz booms peaking 01:00-04:00, with quieter nights for 1-7 days around each full moon. One tagged adult stayed near bottom below 40 m for 2 months, making brief night ascents. Limited to two sites and one tagged fish.

    eastern Gulf of Mexico, SW Florida (outside South Florida) · field · full text read

    Mann et al. 2009
  • Black grouper spawn in late winter, peaking February-March, from full moon to a few days after new moon.

    Black grouper form many small aggregations that move to deeper water off the reef face; pair spawning at dusk; spawning from the full moon to a few days after the new moon on elbows, promontories and shelf-edge reef. Peak February-March.

    Belize (out of region) (outside South Florida) · field · full text re-read Oct 16, 2026

    Paz & Sedberry 2008
  • Billfish and swordfish spawn in summer offshore Gulf water, with larvae densest near the Loop Current edge and fronts.

    Six neuston surveys, June-July 2006-2008, caught 2,888 billfish and 264 swordfish larvae. Sailfish made up 70.4% of billfish larvae and were densest within 100 km of the Loop Current, salinity above 34, SST below 30.5 C. Marlin larvae favored 28-30 C slope water; swordfish below 28.5 C. Larvae only; daytime surface tows.

    northern Gulf of Mexico slope, Alabama to Texas (out of region) (outside South Florida) · field · full text read

    Rooker et al. 2012
  • Black grouper courtship peaks about a week to ten days after the full moon, in late afternoon, during winter and spring.

    Passive acoustics 2012 to 2014 at three aggregations, one on the lower Keys reef and two in Puerto Rico. In Florida, courtship sounds rose 7 to 11 days after full moon, peaking at day 10, and were elevated December to April except January, peaking in April 2012. About 48 percent of calls came 1500 to 1900 hours.

    Florida Keys; Puerto Rico (out of region) (outside South Florida) · field · full text read

    Sanchez et al. 2017
  • Greater amberjack spawn January-June, peaking April-May mainly off south Florida and the Keys; April is closed.

    SAFMC panel document: spawning Jan-Jun, peak Apr-May, mostly off south Florida and Keys near the shelf break. April harvest closure. Commercial landings peak in May at about three times the monthly average; recreational landings mostly in wave 3 (May-Jun), mainly Florida.

    South Atlantic incl. SE Florida and Keys · agency · agency document

    South Atlantic Fishery Management Council 2018
  • Young adult redfish return to spawn in nearshore water off the estuary where they grew up.

    20 subadult red drum tagged in Tampa Bay (2012) and 20 in Charlotte Harbor (2013), tracked 3 years. 74% of Tampa Bay fish reached nearshore adult habitat the year tagged, versus 24% from Charlotte Harbor (65% the next year). Fish from both returned to spawn off their home estuary.

    Tampa Bay; Charlotte Harbor · field · full text re-read Oct 16, 2026

    Walters Burnsed et al. 2020

Habitat

  • In its first year the Vandenberg drew open-water fish such as amberjack, king mackerel and little tunny before reef species moved in.

    REEF surveys April 2009-July 2010: 30 species on the wreck within a month, 100 within six months, 123 by July 2010. Early surveys featured sand and pelagic species (amberjack, juvenile blackfin snapper); later, reef fish. Little tunny, king mackerel and almaco jack were seen only on the Vandenberg. Volunteer sighting frequency: barracuda 86%, yellowtail 78%, amberjack 26%.

    Florida Keys (Key West) · agency · agency document

    Akins 2010
  • Most bonefish stay on their home flats, recaptured within about 5 km, yet travel tens of kilometers to prespawn gatherings.

    Over 7,000 bonefish dart-tagged on three Bahamas islands, with 105 recaptured (1.5%) by guides and anglers. 60-82% were recaptured within 5 km of tagging; mean distance under 11 km. Prespawning sites drew fish from home flats up to 75 km apart, with travel up to 80 km. Accepted manuscript read.

    Bahamas (out of region) (outside South Florida) · field · full text read

    Boucek et al. 2018
  • Baby snook settle first in upstream tidal ponds, then move into the creek at about 40 mm before heading seaward.

    Seining a Tampa Bay-area wetland, September 2006 to February 2007 (480 snook over two years), found young snook densest in upstream ponds (6.8 vs 2.7 fish per 100 m2 in the creek). Fish under 40 mm SL occurred only in ponds; isotopes showed strong site fidelity. Single wetland; second year had few recruits.

    Tampa Bay · field · full text read

    Brame et al. 2014
  • Solution holes with a red grouper held more juvenile reef fish, and a grouper offset the losses a lionfish caused.

    Six-week field experiment in Florida Bay karst solution holes, 4 holes per treatment. Versus holes with no predator, juvenile reef fish fell 83.7 percent with a lionfish alone and rose 154 percent with a red grouper alone. With both predators, numbers matched no-predator holes, and lionfish diets shifted from fish to crustaceans. Small replicate count.

    Florida Bay · experiment · full text read

    Ellis & Faletti 2016
  • West Florida hogfish use both estuary seagrass and nearshore reefs as juveniles; deeper adults likely grew up on nearshore reefs.

    Eye-lens stable isotopes from 27 adult hogfish (27.2 to 74.6 cm) plus muscle from 37 juveniles. Carbon signals separated nearshore (under 30 m) and offshore (30 m or deeper) life histories. Discriminant analysis assigned 51.9 percent of adults to estuarine Cedar Key juvenile habitat, 25.9 percent Tampa Bay and 14.8 percent nearshore Keys. Small sample; 44.9 percent classification accuracy.

    eastern Gulf of Mexico (West Florida Shelf) (outside South Florida) · field · full text read

    Faletti & Stallings 2021
  • Juvenile goliath grouper favor deeper, undercut red mangrove shorelines with overhangs and soft bottom.

    Diver surveys of lower Keys mangrove channels found 52 juveniles (mean 42 cm TL, range 12-110 cm). Presence was tied to sites deeper than about 80 cm, wide overhangs and canopy, soft mud or sand, and concave eroded shorelines; wide prop-root zones were avoided. Visual surveys, partly non-random site selection.

    Florida Keys · field · full text read

    Frias-Torres 2006
  • Tiger sharks roam widely and favor shallow seagrass banks, while reef sharks stay put on the same reefs.

    Acoustic tracking of 23 Caribbean reef and 15 tiger sharks on 13 receivers at two islands over two years. Water depth then habitat type best predicted presence; lunar phase had no effect. Tiger sharks moved between habitats and used shallow seagrass most where it existed; reef sharks showed high site fidelity on deeper reefs.

    Bahamas (out of region) (outside South Florida) · field · full text read

    Gallagher et al. 2021
  • Southeast Florida reefs hold fewer species and fewer young target fish than protected reference reefs; adult target fish are scarce in the Keys too.

    Diver surveys 2016-2018 on reefs shallower than 33 m, compared with a Dry Tortugas reference area. Richness and juvenile target density were lower in SE Florida; adult target density was lower in the Keys and SE Florida (P below 0.001). Mean lengths fell short for 4 of 10 species in the Keys, 4 of 9 in SE Florida.

    SE Florida; Florida Keys; Dry Tortugas · field · full text read

    Grove et al. 2024
  • Bull sharks, great hammerheads and nurse sharks do not avoid the Miami waterfront; many linger near the city.

    Acoustic tracking of 14 great hammerheads, 13 bull and 25 nurse sharks in Biscayne Bay, 2016-2020. Distance to urban areas did not predict residency; stations off South Beach, Government Cut and Dinner Key logged the most sharks. Residency dropped at night and on weekends. Cause of urban residency unknown.

    Biscayne Bay · field · full text read

    Hammerschlag et al. 2022
  • Adult yellowtail snapper are most often found on high-relief reef and the deeper forereef; juveniles use patch reefs.

    RVC 1999-2016 (hard bottom under 30 m). Adults (19 cm FL and up) had highest occurrence on high-relief reef and deep forereef strata; juveniles more on inshore to offshore patch reefs. The January 2010 cold event coincided with a drop in occurrence. Tortugas held more adults than the Keys.

    Florida Keys; Dry Tortugas · agency · agency document

    Herbig et al. 2019
  • Tagged yellowtail snapper kept small home ranges, favored reef edges, and were more often absent in summer and at dusk or night.

    Fifteen yellowtail snapper tracked 2008 to 2009 on 86 acoustic receivers for 1 to 427 days. Six fish showed high site fidelity (mean 58.4 percent). Estimated minimum home range averaged 5.45 km2. Fish preferred reef edge habitat and were more likely absent in summer and at dusk and night. Small sample.

    Dry Tortugas (Florida Keys) · field · full text re-read Oct 16, 2026

    Herbig et al. 2019
  • SE Florida shallow reefs hold far fewer yellowtail, gray snapper and hogfish than Keys reefs; mutton snapper are similar.

    1,360 sites, 0-33 m, May-Oct 2012-2016. Percent occurrence SE Florida vs Keys vs Tortugas: yellowtail 27.9 vs 64.6 vs 80.5; gray snapper 9.3 vs 23.9 vs 19.0; hogfish 23.5 vs 70.3 vs 45.7; mutton 30.1 vs 24.7 vs 39.3. Depth (10 m split), reef type, relief and location drove assemblages.

    SE Florida (Miami-Dade to Martin); compared with Florida Keys and Dry Tortugas · agency · agency document

    Kilfoyle et al. 2017
  • Lightly altered mangrove shorelines near canals and marinas in south Biscayne Bay held fish communities similar to intact mangrove shorelines.

    Comparing six intact and six canal or marina altered mangrove sites (2015-2019), species composition (ANOSIM p=0.60), total abundance (p=0.42) and richness (p=0.25) did not differ. Authors caution alteration was minor and results do not extend to heavily urbanized shorelines.

    Biscayne Bay (southern) · field · full text read

    Lennon & Sealey 2022
  • Juvenile bonefish in Florida estuaries turn up mostly over bare sand or mud and sparse shoal grass.

    FWC monitoring 1996-2019 caught 522 juvenile and 124 larval Albula, over half in the Indian River Lagoon, mostly over unvegetated sand or mud or sparse shoal grass. Modeled ranges were 21.3-33.5 C, oxygen 2.2-13.7 mg/L, salinity 18.0-38.9. Genetics showed mostly A. goreensis, not the sport bonefish.

    Indian River Lagoon; Florida estuaries · field · full text re-read Oct 16, 2026

    Lombardo et al. 2025
  • High-relief Keys reefs hold more reef fish and more species than linear or patch reefs.

    Reef Visual Census data, 5,672 sampling events 1999-2018. High-relief reefs averaged 20-30% higher abundance and about 20% more species than linear and patch reefs; biomass was over twice as high about 2000-2007, then only 20-30% higher. No-take zones led early, but the edge faded after about 2008.

    Florida Keys · field · full text read

    Medina et al. 2021
  • Mutton snapper on SE Florida reefs are mostly sub-adult; median sizes run larger in the Keys and larger again in the Dry Tortugas.

    Diver-estimated median sizes from RVC: SE Florida 37 cm TL (about 10% at or above 50% maturity size), Florida Keys 44.4 cm (about 51%), Dry Tortugas 52 cm (about 77%). Length at 50% maturity 42.2 cm TL.

    SE Florida; Florida Keys; Dry Tortugas · agency · agency document

    Muller & Allen 2023
  • Anglers fishing reef-type bottom in Biscayne National Park caught a mutton snapper on about 1 in 7 trips; most trips caught none.

    Park creel interviews 1978-2022 (13,173 reef-habitat trips, identified by co-caught gray and yellowtail snapper, red grouper, grunts, porgy): mutton caught on 14% of trips; 75th percentile zero, 90th percentile 1 fish. Retained mutton 12.7-93.7 cm. Standardized catch rate was higher after 2007 than before.

    Biscayne National Park · agency · agency document

    Muller 2023
  • Spiegel Grove filled with fish within weeks of sinking; black grouper, barracuda, hogfish and three snappers are regulars on the deep wreck.

    REEF expert surveys 2002-2007 on the 510 ft wreck (deck about 85 ft, sand 130 ft): 46 species within a month, average 76 species per event later, 191 species total. Sighting frequencies over all surveys: hogfish 54%, great barracuda 50%, black grouper 49%, gray snapper 28%, yellowtail 18%, red grouper 17%, greater amberjack 15%, mutton 11%.

    Florida Keys (Key Largo) · agency · agency document

    Reef Environmental Education Foundation 2007
  • The Vandenberg reached most of its fish species list within two years, but stays less diverse than nearby shallow reefs.

    Across surveys since the May 2009 sinking, 84% of total species richness was reached after 2 years. In 2014/2015 the wreck had 105 expert-recorded species, versus 117-131 at shallow reference reefs (three nearby Key West reefs) and 84-109 at deep reference reefs.

    Florida Keys (Key West) · agency · agency document

    Reef Environmental Education Foundation 2015
  • On the Vandenberg, yellowtail snapper were seen on nearly every survey and big barracuda patrol the superstructure.

    REEF July 2014-2015 surveys: yellowtail snapper in 93-100% of surveys; scads and yellowtail made up 82% of 2,508 fish counted in 2014 point counts. Mean sizes: yellowtail about 22-23 cm, great barracuda 87-93 cm, gray snapper about 29 cm, bar jack about 21 cm. Superstructure 40 ft, deck about 100 ft, sand 140 ft; currents usually under 1 kt.

    Florida Keys (Key West) · agency · agency document

    Reef Environmental Education Foundation 2015
  • Shallow coastal ponds ringed by salt marsh and overhanging mangroves are nurseries for juvenile snook, with juvenile tarpon nearby.

    Seasonal seining August 2019 to May 2022 in 22 coastal ponds on the Cape Haze peninsula (651 net sets, 61,702 fish and selected invertebrates). Juvenile snook were most abundant in large, shallow ponds bordered by salt marsh, salterns and overhanging mangroves. Juvenile tarpon overlapped with snook but also used ponds farther inland.

    Charlotte Harbor (Cape Haze peninsula), SW Florida · field · full text re-read Oct 16, 2026

    Saari et al. 2025
  • Six Broward ship reefs at 64-70 ft averaged about 490 fish per count, roughly 3-6 times nearby natural reef edges.

    2000-2001 point counts on the Tracy, Merci Jesus, Jay Scutti, Peter B. McAllister, Robert Edmister and an unnamed barge: mean 491 fish per count vs 146 on the middle reef east edge and 79 on the outer reef west edge; Amberjack on Edmister (35) and McAllister (20); cobia on McAllister and the barge. Richness peaked December, biomass January.

    SE Florida (Broward) · agency · agency document

    Spieler 2001
  • Off Miami-Dade, high-relief limerock boulder reefs held more gamefish species than low, spread-out module or single-layer boulder reefs.

    2019 re-survey of 7 county reefs (25-68 ft, deployed 1993-2005): gamefish richness 12 at Golden Beach Boulders, 11 at Anchorage Boulders and Port of Miami B Rows, 5-6 at Sunny Isles reefs. Lane snapper 451, yellowtail 131, hogfish 55 (none legal), 4 black grouper. Tomtate schools drove densities of 8.9-14.9 fish/m2 on two boulder reefs.

    SE Florida (Miami-Dade) · agency · agency document

    Thanner et al. 2019
  • The Port of Miami limerock boulder rows and piles at 45 ft were the most species-rich county artificial reefs in the earlier survey.

    In Miami-Dade's re-evaluation, Port of Miami B Piles and B Rows (limerock boulders, 45 ft, deployed 1996 as dredging mitigation) had 67 and 66 resident species in the previous survey, the highest, and the highest diversity and evenness. They also had more octocorals. In 2019, B Rows held 11 gamefish species and B Piles 9.

    SE Florida (Miami-Dade) · agency · agency document

    Thanner et al. 2019

Depth

  • Bigger Gulf tiger sharks move off the shelf into deep water in fall and winter; small ones stay on the shelf.

    SPOT tags on 56 tiger sharks, 2010-2018. Small sharks under 200 cm stayed on the shelf (91% of positions), often nearshore Florida in summer. Large sharks over 250 cm used slope water 31% of the time, shifting deeper October-April. Mean underlying depth was 1240 m in fall versus 363 m in summer. Most sharks were immature.

    Gulf of Mexico (outside South Florida) · field · full text read

    Ajemian et al. 2020
  • Swordfish follow the deep prey layer day to day, while blue marlin and yellowfin rarely spend time below 200 m.

    344 tags on 12 predator species (46,659 tracking days) showed every species reached past 900 m. Daily time deeper than 200 m was under 5% for blue marlin, yellowfin and tiger shark. Swordfish depth tracked the modeled deep scattering layer on 51% of days, largely independent of temperature. Prey layer depth was modeled, not measured, for most comparisons.

    North Atlantic basin · field · full text read

    Braun et al. 2023
  • Blue marlin sit at the surface at night but spend much of the day deeper, often 40 to over 100 m, with quick surface trips.

    51 satellite tags on released blue marlin showed about 50% of night time in the top 10 m versus under 20% by day; time at or below 100 m was under 2% at night and about 17% by day. Recovered tags showed 91% of night time in the top 5 m versus 22% by day. Individuals varied widely.

    western North Atlantic and Caribbean · field · full text read

    Goodyear et al. 2008
  • Red grouper and scamp are the main game fish on the Pulley Ridge mesophotic reef at about 60-105 m.

    ROV surveys 2012-2015 over 208 red grouper pits at 59-106 m. Red grouper in 35-46% of pits (50-80 cm TL, mean 60 cm), at most one per pit; red grouper and scamp were the most abundant economic species (0.40 and 0.35 per pit). Bottom temperature 18-29 C.

    Pulley Ridge, SW Florida shelf (Gulf) · field · full text read

    Harter et al. 2017
  • Red grouper move from shallow reefs to water deeper than about 36 m as they mature.

    Summary of Moe 1969 tagging in an agency report: juveniles and subadults live at 3-18 m; around 40-45 cm SL and 4-6 years they shift offshore to over 36 m; usual maximum habitat depth about 120 m, with reports below 200 m. Tagged adults moved 28-72 km.

    SE Florida; eastern Gulf (literature summary) · agency · agency document

    Kilfoyle et al. 2017
  • On SE Florida reefs shallower than 33 m, few snapper are legal size and large groupers are rare.

    Share of fish at or above legal size: mutton 10.7%, yellowtail 8.6%, gray snapper 31.8%, lane 48.3%, hogfish 24.6%. Only 22 black grouper, 15 gag, 35 scamp and 46 amberjack counted in five years. Several deep groupers and snappers absent at 0-33 m have been documented at 50-120 m off Broward.

    SE Florida, reef 0-33 m · agency · agency document

    Kilfoyle et al. 2017
  • Most yellowtail snapper caught on Florida charter and head boats come from water shallower than 20 m.

    At-sea observers 2010-2017: mean capture depth of discarded yellowtail 10-26 m on headboats (max 53 m) and 8-17 m on charters (max 85 m); largely under 20 m. Good release condition 85.6% (headboat) and 79.1% (charter); immediate mortality under 2% in every region.

    Florida Keys and SE Florida (for-hire) · agency · agency document

    Lazarre 2019
  • Keys charter boats catch most mutton snapper shallower than 10 m; SE Florida boats catch them mostly at 20-39 m.

    At-sea observers 2009-2022, share of released mutton by depth. Keys charter: 76.5% at 0-9 m (headboat 54.0% at 0-9 m, 27.0% at 10-19 m). SE Florida charter: 92.3% at 20-39 m; headboat 61.6% at 20-39 m plus 16.0% at 40-49 m. Private-angler release share fell from about 95% at 0-9 m to 51-55% at 60-79 m.

    Florida Keys; SE Florida · agency · agency document

    Lazarre 2023
  • Wahoo mostly stay above 50 m, while swordfish sit near the surface at night and drop to 700-800 m by day.

    Review of conventional and electronic tagging: blue marlin and yellowfin mainly stay in the warm surface layer (marlin occasionally below 300 m); wahoo show less vertical range, mostly above 50 m; swordfish follow the deep scattering layer, within about 20-30 m of the surface at night and 700-800 m by day. Wahoo electronic data were scarce.

    western North Atlantic and wider Caribbean · review · full text re-read Oct 16, 2026

    Luckhurst 2007
  • On Keys reefs, mutton snapper are seen more often at deeper, more seaward stations than on shallow patch reefs.

    FWC analysis of NOAA/UM Reef Visual Census (RVC, stations to 33 m). Keys: mutton seen at 19% of 10,135 stations; mean depth where seen 11.3 m vs 8.0 m where absent. SE Florida: seen at 35% of 3,530 stations (median station depth 16 m). Dry Tortugas: 30% of stations, no depth effect.

    Florida Keys; SE Florida; Dry Tortugas · agency · agency document

    Muller & Allen 2023
  • Hogfish occur on over half of surveyed Keys reef sites, favoring slightly deeper, higher-relief seaward reef.

    RVC 1997-2024: hogfish seen at 55% of 9,616 Keys stations, mean station depth 8.4 m where seen vs 6.9 m where absent; habitat and rugosity were the top predictors. SE Florida 2013-2024: seen at 33% of 3,809 stations. Median size 23-24 cm FL; larger fish assumed deeper than 30 m.

    Florida Keys; SE Florida · agency · agency document

    Muller & O'Farrell 2025
  • Gray snapper are common on Keys reefs to 30 m, but larger adults also live deeper than divers survey.

    Gray snapper seen at 22.5% of 13,607 RVC stations (1997-2018). Median diver-estimated size 24 cm TL; 29% at or above 30.5 cm. Depth category, habitat and reef zone predicted presence. Author used dome selectivity because the species ranges deeper than the 30 m survey limit. Counts of 350-1,605 fish likely spawning aggregations.

    Florida Keys; Dry Tortugas · agency · agency document

    Muller 2022
  • After about three years, the Spiegel Grove fish community resembled nearby deep reef ledges more than shallow reefs or the Benwood.

    Year to year species overlap on the wreck stayed near 50% early on, then rose toward natural reef levels about 3 years after sinking (2005). By 2007 composition was most similar to deep natural ledges (Dixie Ledge, Red Can Ledges) and least similar to shallow reefs and the 1942 Benwood wreck, which had 196 species.

    Florida Keys (Key Largo) · agency · agency document

    Reef Environmental Education Foundation 2007

Tide

  • Weekly water level departures from the tide can be forecast with skill out to 2 to 3 weeks.

    Subseasonal reforecasts (2000-2019) of non-tidal residual water level at U.S. gauges beat damped persistence through 2 to 3 weeks, IFS up to 6 weeks; Gulf stations kept correlation near or above 0.5 to week 6. Damped persistence used the previous 7-day mean anomaly times each station's lead-dependent autocorrelation. Adding the inverse barometer effect helped weeks 1 to 2.

    U.S. coastal tide gauges incl. Virginia Key, Vaca Key, Key West, Naples · model · full text read

    Albers et al. 2025
  • Bonefish were most active at dawn, on ebbing and low tides and in cooler 22-25 C water, and fed mostly at night.

    Accelerometer loggers on 5 bonefish over 5 days in an Eleuthera wetland pond cut off from the sea. Fish rested 57% of the time and fed about 11 times per hour. Activity peaked at dawn and in 22-25 C water, and was highest on ebbing and low tides, lowest on flood. Tiny sample; tide signal may be an internal rhythm.

    Bahamas (out of region) (outside South Florida) · field · full text read

    Brownscombe et al. 2014
  • A water level forecast is only worth showing if it beats the tide table plus today's offset.

    NOS requires model water level and current forecasts to beat (1) astronomical tide prediction alone and (2) tide prediction plus a persisted non-tidal offset observed before forecast time; for temperature, salinity and non-tidal water level, the model must beat another method. A model that is no improvement should not be implemented.

    U.S. coastal (NOAA standard) · agency · agency document

    Hess et al. 2003
  • Reef sharks in a tidal pass were most active at night, on outgoing current and around full and new moons.

    Depth and accelerometer tags on 38 gray reef sharks in a Fakarava atoll pass, July 2017-June 2018. Sharks used more space and were more active at night and on outgoing currents, and activity peaked at full and new moon. They swam deeper by day (about 18.6 m) than night (16.1 m). Effects were modest; individual differences explained more.

    French Polynesia (out of region) (outside South Florida) · field · full text read

    Laurioux et al. 2024
  • A weaker Florida Current raises South Florida water levels by about 1.4 cm per Sverdrup.

    Geostrophic balance links Florida Current transport to coastal sea level at about -1.4 cm per Sv. A 3 Sv transport decline (2004-2014, EMD trend) matched mean sea level rises of 7.4, 7.1 and 5.9 cm at Vaca Key, Florida Bay and Virginia Key; annual transport and sea level cycles correlated at -0.86 to -0.92.

    Florida Straits, Florida Bay and Keys tide gauges · field · full text read

    Park & Sweet 2015
  • In eastern Florida Bay the tide is only a few centimetres; wind, not tide, sets water depth.

    A 3-D model validated with 1993-1994 water level data showed M2 tidal amplitude damped to about 1 to 5 cm in the very shallow eastern bay (depths generally under 50 cm), about 1 cm with wetting and drying; tidally averaged setup in the eastern bay drives southward residual flow through Keys channels.

    Florida Bay · model · full text read

    Sheng & Davis 1997
  • Estuary bream were most active on daytime high tides and least active at night, and moon phase added nothing.

    Accelerometer tags on 6 yellowfin bream for about four months in 2011. The best model kept light, tide, depth and a light-by-tide interaction: activity was lowest at night regardless of tide and highest on daytime high tide. Lunar phase (P = 0.47), turbidity and temperature dropped out. Small sample, winter period.

    Australia (out of region) (outside South Florida) · field · full text read

    Taylor et al. 2013

Current

  • Spring larval tuna and mahi numbers in the central Gulf rose and fell with how far north the Loop Current reached.

    Altimetry 1992-2008 matched to 1,632 spring SEAMAP stations, 1993-2007. In a box at 26N 87W, combined larval density of five pelagic taxa tracked Loop Current northward excursions (R2 0.71). Bluefin and Auxis larvae were denser at anticyclone boundaries, about 148-158 cm sea surface height. Larvae only; no link outside the current's reach.

    northern Gulf of Mexico (outside South Florida) · field · full text read

    Lindo-Atichati et al. 2012
  • The Florida Current carries about 32 million cubic meters per second, strongest in July and weakest in January.

    25-year cable record at 27 N: mean transport 32.1 Sv, standard deviation about 3.3 Sv; annual cycle amplitude about 0.9 Sv with maximum in July and minimum in January. Day-to-day variability far exceeds the seasonal signal.

    Northern Straits of Florida (27 N) · field · full text read

    Meinen et al. 2010
  • Water inside a Florida Straits eddy held far more larval fish and copepods than nearby Florida Current water.

    A towed imaging system (132 million plankton images) crossed a decaying cyclonic eddy edge in June 2015, days before it dissipated. Larval fish and Oithona copepods were significantly denser in eddy water than Florida Current water, with patches tightly overlapping. Current speed and direction, not feeding, mainly explained distributions. One eddy; prey base, not gamefish.

    Florida Straits · field · full text read

    Schmid et al. 2020
  • Gulf yellowfin catches stay fairly steady year-round and show little link to eddies or surface temperature, unlike bluefin.

    Observer longline data (1993-2005) plus tagging cruises: yellowfin catch rate ranged from 5.48 per 1000 hooks in March to 12.8 in July (monthly CV 0.26 versus 1.38 for bluefin). SST and sea height anomaly dropped out of the yellowfin model; lower wind and deeper water went with higher catch. Bluefin favored cool cyclonic eddies. Commercial gear.

    Gulf of Mexico (outside South Florida) · field · full text read

    Teo & Block 2010
  • A cold Tortugas eddy sat off the lower Keys for about three months, greener than surrounding water and 2-4 C cooler below the surface.

    Satellite, Argo, ship ADCP and HYCOM data tracked a cyclonic eddy formed April 9, 2017 that stayed off the lower Keys from April 23 to July 15. It averaged about 100 km across and reached about 800 m deep. Chlorophyll was higher; subsurface water was 2-4 C cooler, but summer surface temperature showed little difference. Single eddy.

    Florida Straits, lower Keys · field · full text read

    Zhang et al. 2022

Fronts and edges

  • Juvenile tarpon leave shallow mangrove nursery creeks when water drops below about 20 C, not in response to water levels.

    Tagged juvenile tarpon (25-35 cm TL) entered restored mangrove habitat within 3 days of construction. Emigration from juvenile habitat was significantly related to temperatures below 20 C, not water level; half emigrated in one winter and the rest a year later.

    Restored mangrove creeks, south Florida · field · full text re-read Oct 16, 2026

    Kendall et al. 2025
  • Tagged tuna, marlin and sailfish spent much of their time on ocean fronts and eddy edges, including the Florida Current edge.

    Rebuilding 124 satellite-tag tracks with ocean heat content showed 52.4% of tuna, marlin and sailfish spent over 60% of their time on fronts and eddies, though these covered only about 18% of available habitat (2009-2013). A Keys sailfish rode the Florida Current edge, then the Loop Current edge. Method paper; habitat association, not catch.

    Gulf of Mexico and western North Atlantic (outside South Florida) · field · full text read

    Luo et al. 2015
  • In Gulf longline data, satellite temperature breaks alone did not predict where yellowfin tuna were caught.

    Compared 6,618 longline sets, 1986-1987, with 109 satellite SST images. Mean catch was 14.2 yellowfin per 1000 hooks and 79.2% of sets caught at least one. No relation appeared between catch rate and local SST, SST variability or gradient. Caveat: only one position per set, and lines can exceed 50 miles.

    northwestern Gulf of Mexico (out of region) (outside South Florida) · field · full text read

    Power & May 1991

Floating weed

  • Cyclonic eddies in the Atlantic Sargassum belt hold more weed than nearby water, mostly in their centers.

    Daily MODIS Sargassum maps (3 km) and altimetry eddies from 2011-2023 showed cyclonic eddies held 6-47% more Sargassum than eddy-free water in all five regions, concentrated within half an eddy radius of the center. Warm eddies varied. Bigger, stronger eddies held more; density fell in winds above about 7.2 m/s. Weed only, no fish.

    tropical Atlantic and Caribbean (out of region) (outside South Florida) · field · full text read

    Zhang et al. 2025

Salinity

  • Young tarpon tolerate salinity from near fresh to over 40 ppt and water up to at least 36 C.

    Review of flats fishes and climate: juvenile tarpon in coastal marsh nurseries withstand salinities near zero to over 40 ppt and temperatures to at least 36 C, and gulp air under near-anoxic conditions. Abrupt drops over 7 C below ambient can impair bonefish and other flats fishes.

    Review, flats fisheries (incl. Florida) · review · full text read

    Danylchuk et al. 2023
  • Florida Bay fish kills in 2015 came with bottom water above 65 PSU and 38 C.

    Late summer 2015 salinities in Rankin Lake, Johnson Key and Whipray basins hit 15-year highs above 50-60 PSU for weeks; where fish kills occurred, bottom water exceeded 65 PSU and 38 C under stratification (surface about 50 PSU, 35 C). NPS reported two July 2015 kills of toadfish and pinfish; about 88 km2 of seagrass died.

    Florida Bay (north-central basins) · field · full text re-read Oct 16, 2026

    Hall et al. 2016
  • Young bull sharks avoid water fresher than about 7 PSU and move upriver when the river runs saltier.

    56 young bull sharks tracked up to 460 days in the Caloosahatchee. They avoided salinity under 7 and favored 7 to at least 20 (switch point 8 for all years). Mean river position tracked salinity; at flows above 113 m3 per second they stayed near the mouth, but spread through the river below 57. Temperature mattered little.

    Charlotte Harbor (Caloosahatchee River) · field · full text read

    Heupel & Simpfendorfer 2008
  • Juvenile spotted seatrout abundance peaks near 17 to 20 ppt salinity and rises with warmth up to about 28 C.

    GAMs on FWC seine data from three Florida estuaries: unimodal salinity effect peaking at 20 ppt (IRL), 17 ppt (Tampa Bay), 18 ppt (Charlotte Harbor). Abundance increased with temperature to 28 C, then declined in IRL, kept rising in TB, flat in CH. Seagrass and sand-mud bottoms were most productive.

    Indian River Lagoon, Tampa Bay, Charlotte Harbor · model · full text read

    Kupschus 2003
  • Along southern Biscayne Bay mangrove shorelines, gray snapper make up nearly half of fish biomass, with barracuda and snook next among gamefish.

    NOAA IBBEAM visual transects (30 x 2 m) at 12 shoreline sites, 2015-2019, dry and wet seasons: 16,752 fish of 36 taxa analyzed. Mojarras were 45% of numbers; gray snapper 11% of numbers but 46% of biomass; barracuda 9% and snook 4% of biomass. Assemblages split by salinity (higher, steadier) and depth, not by shoreline type.

    Biscayne Bay (southern) · field · full text read

    Lennon & Sealey 2022
  • West-central Florida Bay commonly reaches 40 to 50 PSU by late dry season and has hit 70 PSU.

    Review of die-off drivers: salinities of 40-50 PSU are frequent at the end of the dry season (April-May) in west-central Florida Bay, with 70 PSU recorded. Seagrass photosynthesis declines above about 60 PSU, oxidation stress risk rises above 55 PSU, and water above 33 C breaks down seagrass physiology.

    Florida Bay · field · full text re-read Oct 16, 2026

    Madden et al. 2024
  • In the southern Indian River Lagoon, clearer, saltier water near inlets held more shark and ray species; bull sharks dominated near freshwater outflows.

    Fishery-independent survey 2016-2018 caught 630 elasmobranchs of 16 species. Bull sharks and Atlantic stingrays were each over 20% of catch, most abundant in fall; bull sharks most common near Vero Beach and the St. Lucie River. Diversity rose in clearer, deeper, saltier water nearer inlets and farther from freshwater sources.

    Southern Indian River Lagoon (Sebastian to St. Lucie Inlet) · field · agency document

    Roskar et al. 2020
  • Juvenile tarpon in Texas bays are most likely in fresh to brackish water below about 20 PSU and at 20 to 27 C.

    GAMs on four decades of TPWD gillnet data: tarpon presence higher in fresh and brackish water, declining as salinity rose to about 20 PSU; presence rose with temperature to about 22 C and turned negative near 27-28 C. DO was not important in most models, attributed to air breathing.

    Texas bays, northern Gulf (out of region) (outside South Florida) · model · full text read

    Stephens et al. 2024

Dissolved oxygen

  • Florida law sets marine oxygen standards at 42 percent saturation daily, 51 weekly and 56 monthly.

    Rule 62-302.533 F.A.C.: in predominantly marine Class II and III waters, daily average DO saturation shall not fall below 42 percent in more than 10 percent of values; 7-day average 51 percent; 30-day average 56 percent. Peninsula and Everglades fresh waters use 38 percent.

    Florida (state rule) · agency · agency document

    Florida Administrative Code 2013
  • Florida treats daily oxygen under 2.8 mg/L as lethal risk and over 4.9 mg/L as fully protective.

    Using the EPA Virginian Province approach with Florida species, DEP derived a juvenile/adult survival criterion (CMC) of 2.8 mg/L (about 42 percent saturation) and a growth criterion (CCC) of 4.9 mg/L (about 64 percent saturation); between them, exposure duration limits apply via a larval recruitment curve.

    Florida marine waters (agency) · agency · agency document

    Florida Department of Environmental Protection 2013
  • Lethal oxygen for half of tested fish: red drum 1.45, pompano 1.74, spotted seatrout 1.88 mg/L.

    Florida DEP compiled acute low-DO LC50s for 26 marine species. LC50s: red drum 1.45, striped mullet 1.38, pinfish 1.61, Florida pompano 1.74, spotted seatrout 1.88, scaled sardine 2.17 mg/L. Pompano and seatrout were among the four most sensitive species.

    Florida (agency synthesis) · agency · agency document

    Florida Department of Environmental Protection 2013
  • The August 2020 Biscayne Bay fish kill came with oxygen as low as 0.2 mg/L, 29-33 C water, calm winds and low tides.

    Miami-Dade summary: the 4-11 August 2020 kill in two northern Biscayne Bay basins had surface DO of 0.2-3 mg/L, water 29-33 C, winds under 3.5 m/s, high nutrients and long residence time, killing bottom fish. A 2021 kill covered 4 basins. About 70% of seagrass (about 64 of 91 square km) was lost in affected areas.

    North Biscayne Bay, Miami-Dade · agency · agency document

    Miami-Dade County Department of Regulatory and Economic Resources 2021
  • In lab tests the mean sublethal oxygen threshold across 34 fish experiments was 4.4 mg/L, well above the 2 mg/L hypoxia label.

    Meta-analysis of benthic marine organisms: fish mean LC50 1.54 mg/L (90th percentile 2.51), mean sublethal SLC50 4.41 mg/L (90th percentile 8.09), mean LT50 59.9 h. Across all taxa, 90th percentile LC50 was 4.59 mg/L; the conventional 2 mg/L hypoxia line is below thresholds for half of species.

    Global meta-analysis (outside South Florida) · review · full text re-read Oct 16, 2026

    Vaquer-Sunyer & Duarte 2008

Water clarity

  • Keys water got clearer offshore since 1995, but Upper Keys inshore and backcountry bottoms now get less light.

    Turbidity declined throughout the FKNMS over 31 years, most in the northern Sluiceway, Backcountry and Marquesas, with increases at some Upper Keys shore sites. Kd fell offshore and at the Marquesas but rose at isolated Backcountry, Sluiceway, shore and inshore sites; Upper Keys inshore lost bottom light. No significant salinity trend.

    Florida Keys · agency · agency document

    Briceno & Boyer 2026
  • EPA targets for Keys reefs: chlorophyll a at or under 0.35 ug/L and light attenuation at or under 0.20 per meter.

    EPA Strategic Targets (SP-47) for the FKNMS, judged against a 1995-2005 baseline: reef sites chlorophyll a 0.35 ug/L or less and Kd 0.20 per m or less; all sites DIN 0.75 uM (10.5 ppb) or less and TP 0.25 uM (7.7 ppb) or less. Kd has met target since 2006; chlorophyll was elevated 2017-2022 and returned lower 2023-2025.

    Florida Keys · agency · agency document

    Briceno & Boyer 2026
  • In very murky water, a sight-feeding reef fish took longer to start searching, swam farther and found food less efficiently.

    Aquarium trials with Picasso triggerfish (4 fish analyzed) at high turbidity (40 to 68 NTU) versus low (0.4 to 1.4 NTU). In murky water fish waited 26.8 s longer to start, needed 111.5 s more total foraging time and swam 3.5 m farther on more tortuous paths. Indo-Pacific species, tiny sample, lab only.

    Laboratory aquarium (out of region) (outside South Florida) · experiment · full text read

    Newport & Padget 2021

Runoff and freshwater flow

  • Record storm runoff that cooled, freshened and drained oxygen from an estuary pushed resident fish out to the coast.

    Acoustic tracking of 43 striped bass through Tropical Storms Irene and Lee, 2011, versus a normal 2010. River discharge hit 4,471 m3/s versus about 269 in a normal August. Temperature, salinity and oxygen fell in the lower estuary, and fish moved downriver and out to the coast; some made later scouting trips back. Not a Florida species.

    Hudson River, New York (out of region) (outside South Florida) · field · full text read

    Bailey & Secor 2016
  • After heavy 2015 rain and St. Lucie releases, turbid water came offshore yet reef schools and goliath grouper spawning persisted.

    After a September 2015 heavy rainfall and freshwater release, water-column backscatter rose about 12,000 percent; school backscatter rose 172 percent and schooling density 182 percent, then fell after the perturbation. Goliath grouper courtship sound continued throughout the turbid period.

    SE Florida nearshore reefs (St. Lucie discharge) · field · full text read

    Binder et al. 2023
  • Phosphorus has risen near Keys shorelines since 1995 while nitrogen and organic carbon fell.

    Surface TP rose significantly at 48 sites, mostly close to land (median +0.002 mg/L, about 44 percent over 1995), pointing to land sources; deeper surrounding waters declined. TN declined except in the Sluiceway next to Florida Bay; TOC (a CDOM proxy) fell until about 2005. DIN and TP both rose Keys-wide in 2025.

    Florida Keys · agency · agency document

    Briceno & Boyer 2026
  • Plumes from Miami and Broward inlets drift mostly north but also reach tens of kilometers south, worst in the wet season.

    SLIM ocean model, September 2018 to August 2021, releasing inlet water from Government Cut, Haulover, Port Everglades and Hillsboro using SFWMD flows. Plumes ran mostly north but had southern footprints of tens of km. Government Cut had a bigger footprint and load than the other inlets modeled. Concentrations were higher in the wet season, May to October. Model only.

    SE Florida · model · agency document

    Dobbelaere et al. 2024
  • Since January 2026 Florida law bars routine sewage discharge from SE Florida ocean outfalls; only wet-weather backup flows remain.

    Florida Statute 403.086(10) prohibits domestic wastewater discharge through ocean outfalls after December 31, 2025, except backup discharges within a functioning reuse system, mainly in wet weather; peak-flow backups are capped at 5 percent of baseline flow (5 year rolling). Outfall effluent had to meet advanced treatment (TN 3 mg/L, TP 1 mg/L annual average) by 2018.

    SE Florida (Miami-Dade, Broward, Palm Beach) nearshore Atlantic · agency · agency document

    Florida Legislature 2025
  • During big freshwater releases snook move more and slide into slower side waters, but do not leave the estuary.

    Acoustic telemetry of 279 tagged snook in the St. Lucie Estuary, 2008-2014, across four high-discharge events. No large synchronized exodus; snook were more likely to move during discharges and with bigger salinity changes in either direction. Fish 602-786 mm TL used a slower-flow tributary. Individual behavior varied.

    St. Lucie Estuary (SE Florida) · field · full text re-read Oct 16, 2026

    Kleiman et al. 2026
  • Nitrate on SE Florida reefs spikes after strong inlet outflow, and phosphorus rises after rain.

    Monthly bottom water samples at 29 reef sites, 2018 to 2021, modeled with boosted regression trees against inlet outflow, rain and wind. Nitrate peaked when summed inlet flow was 75 to 100 m3/s over 3 days and rain topped 50 mm. Orthophosphate peaked near 200 mm of rain over 14 days. Suspended solids were poorly explained. No fish data.

    SE Florida · field · full text read

    Whitall et al. 2025

Red tide and algal blooms

  • Keys chlorophyll has crept up about a third since 1995 at some sites, mostly shallow water near land.

    Over 1995-2025 (122 quarterly surveys, 112 stations in 2025), chlorophyll a rose significantly at 17 of 112 sites by 0.06 to 0.14 ug/L (median 0.10), about 37 percent above 1995, strongest at shallow nearshore stations but also some offshore reefs and passes. Authors call it slow eutrophication.

    Florida Keys · agency · agency document

    Briceno & Boyer 2026
  • Red tide above 10,000 cells per liter can cause fish kills and breathing irritation; above 100,000, fish kills are probable.

    FWC Karenia brevis key: background 1,000 cells/L or less (no effects); very low over 1,000-10,000 (possible respiratory irritation, shellfish closures from 5,000); low over 10,000-100,000 (possible fish kills); medium over 100,000-1,000,000 (probable fish kills, satellite-visible chlorophyll); high over 1,000,000 (plus water discoloration).

    Florida statewide (Gulf and Atlantic coasts) · agency · agency document

    Florida Fish and Wildlife Conservation Commission, Fish and Wildlife Research Institute
  • Satellite color data can map Indian River Lagoon brown tide closely enough to track blooms early, especially in the Banana River.

    Varimax principal component analysis of 12 Sentinel-3A OLCI images over about 1.5 years, checked against a hand spectroradiometer and water samples at 11 sites. The brown tide component tracked Ochrophyta biovolume with R2 of 0.92 (satellite, 300 m pixels) and 0.93 (field). Bloom was concentrated in the Banana River. Method study; no fish data.

    Indian River Lagoon · field · full text read

    Judice et al. 2020
  • Severe red tides knock down shelf fish biomass and catch, with 2005 the worst year; young gag take the heaviest hit.

    Ecospace ecosystem model with lethal and sublethal red tide responses, 2002-2020. Biomass loss peaked in 2005, then 2018, 2019, 2006 and 2012. For gag, 71 of 160 scenarios passed validation; red tide mortality was highest in 2005 and fell hardest on younger fish. Survey checks in 2005, 2014 and 2015 confirmed declines inside bloom areas. Model, not direct counts.

    West Florida Shelf · model · full text read

    Vilas et al. 2023

Rain

  • Large bull sharks appear off beaches more when water is above 20 C, after heavy rain, and in moderate 1.8-2.8 m swell.

    233 tagged bull sharks and 21 beach receivers, 2017-2023. Large sharks occurred more when water exceeded 20 C (peak 23 C), after more than 45 mm of rain, and in 1.8-2.8 m swell; moon and tide had no effect. Top stations sat within 800 m of river mouths. Juveniles were not detected until 157 cm.

    New South Wales, Australia (out of region) (outside South Florida) · field · full text read

    Smoothey et al. 2023

Sea state

  • Offshore wave height forecasts are typically within about 0.4 m on day 1, degrading most between days 4 and 10.

    A 20-year GEFSv12 WAVEWATCH III reforecast verified against offshore buoys (coastal sites excluded) gave significant wave height RMSE 0.37 m and correlation 0.95 on day 1, ensemble-mean RMSE 0.57 m and correlation 0.88 in week 1, 0.87 m and 0.70 in week 2; bias near zero. Scatter error grew mostly between days 4 and 10.

    Global offshore buoys (NDBC and Copernicus) (outside South Florida) · model · full text read

    Campos et al. 2024

Cold fronts

  • Juvenile redfish make longer bay moves when water drops below 16 C and salinity is falling, conditions that followed winter fronts.

    Acoustic arrays in Christmas Bay, Jan-May 2012, with 14 juvenile red drum. Odds of moving over 1 km rose on days salinity was falling, when salinity was above 25, and below 16 C. Authors tie falling salinity to winter cold fronts. Max daily move 7.7 km. Fronts were not modeled directly.

    Texas (out of region) (outside South Florida) · field · full text read

    Dance & Rooker 2015

Barometric pressure

  • Juvenile tarpon leave isolated mangrove ponds on low pressure and high water; distant ponds need tropical storm flooding to let them out.

    Acoustic telemetry of juvenile tarpon in coastal ponds on the Cape Haze peninsula. Emigration rose with low barometric pressure, high water level and larger body size. Ponds near tidal creeks drained fish on summer king tides; ponds farther inland needed tropical cyclone conditions. Fish later appeared at river mouths about 30 km up-estuary. Pressure effect not given as a threshold.

    Charlotte Harbor · field · full text re-read Oct 16, 2026

    Bunting et al. 2024
  • In lab tests, fish learned a feeding depth and found it again using water pressure alone.

    Lab trials with Mexican tetras. Ten of 27 fish learned a food site depth with visual cues scrambled. When water was added to change pressure, fish shifted their search depth as predicted in 17 of 30 trials, for example 15 cm higher after 15 cm was added. Hydrostatic, not weather, pressure; mechanism only.

    laboratory (out of region) (outside South Florida) · experiment · full text read

    Davis & Holbrook 2021
  • Tagged red snapper were far more likely to leave their home reef on low-pressure storm days.

    Acoustic positioning of 71 red snapper at 34-38 m, 101 km offshore, 2020-2022. Low-pressure days (below 1007.96 mb) raised daily emigration probability to 0.072 from 0.00041, about 175 times. Departures also clustered in May-June and Sept-Oct. Annual site fidelity was 54-63%; one fish dispersed 206 km.

    West Florida Shelf · field · full text read

    Lowerre-Barbieri et al. 2025
  • Young blacktips left a Tampa Bay nursery before a tropical storm, about when pressure fell to 1007 hPa and wind reached 25 km/h.

    Acoustic tracking of 14 juvenile blacktips (54-61 cm) in Terra Ceia Bay during Tropical Storm Gabrielle, Sept 2001. Half had left when pressure hit 1007.4 hPa and wind 24.6 km/h; none were inside 3-6 h before landfall. Fish stayed outside about 6-7 days, were back about 21 days later; 10 of 14 returned. Australian species were analysed too.

    Tampa Bay · field · full text read

    Udyawer et al. 2013

Hurricanes and storms

  • Inshore fish calling dropped to its lowest at a tropical storm's peak, then jumped to its highest right after it passed.

    Passive acoustic recorders inside Tampa Bay and offshore during Tropical Storm Debby, June 2012 (pressure low 1002.2 mb, surge 1.17 m). Storm noise rose up to 13.5 dB. Inshore, total calls fell lowest at the storm peak and peaked afterward, led by sand seatrout and silver perch. Spotted seatrout and red drum calls were too rare to test.

    Tampa Bay; eastern Gulf of Mexico (outside South Florida) · field · full text read

    Boyd et al. 2021
  • Sharks briefly left a nursery during a tropical storm; a sudden water temperature drop was the strongest cue, falling pressure secondary.

    Acoustic array tracking 22 juvenile white sharks through Tropical Storm Hilary, Aug 2023. Water temperature fell 6 C in 12 hours. Hourly sharks detected fell from 16-19 to 8; emigration probability peaked at 0.311 versus 0.011 baseline. Falling SST was the top predictor; waves, falling pressure and salinity were secondary. Nearly all returned within three weeks.

    Southern California (out of region) (outside South Florida) · field · full text read

    Elstner et al. 2026
  • During two Category 5 hurricanes, tagged nearshore fish shifted briefly toward deeper water, but most stayed in the bay for months.

    Acoustic array in Brewers Bay, St Thomas, during Irma and Maria, Sept 2017. Six fish (lane, mangrove and mutton snapper, tarpon) and four southern stingrays were tagged. Several moved toward deeper water and widened their range the week after Irma; all fish stayed over 14 weeks, but two stingrays left. Water cooled about 2 C and oxygen fell 1-2 mg/L.

    US Virgin Islands (out of region) (outside South Florida) · field · full text read

    Matley et al. 2019
  • Young bull sharks fled the Shark River ahead of Hurricane Irma as pressure fell, and most came back within weeks to months.

    Acoustic tracking of 14 juvenile bull sharks, 2016-2018. Eleven left between 17 days before and 1 day after Irma; nine returned after about 55 days, six having been detected about 80 km north. Three youngest sharks likely died. Falling pressure and faster pressure change best predicted departure; river stage effect was weak.

    Everglades (Shark River Estuary) · field · full text read

    Strickland et al. 2019
  • Summer storms that mixed and warmed bottom water cut reef fish movement by about half, and late storms pushed some off reefs.

    Acoustic tracking of 8-15 black sea bass per year at three reefs, 2016-2018, paired with an ocean model. Six storms broke up stratification, warming bottom water 5.7-10.9 C. Activity fell about 50% after storms, and some fish left reefs for good. Bottom warming was the main driver; turbulence and current were smaller effects.

    Mid-Atlantic Bight (out of region) (outside South Florida) · field · full text read

    Wiernicki et al. 2020
  • Juvenile fish in seagrass mostly held up through tropical storms, but the strongest storms brought the biggest short-term drops.

    Monthly trawls in Back Sound seagrass, 2010-2020, across ten tropical cyclones, before-after-control-impact design. On average catch and richness were not altered. Storm energy correlated with bigger short-term declines (R2 0.52 for catch), with Hurricane Florence worst. Seagrass looked largely undamaged. Juveniles only.

    North Carolina (out of region) (outside South Florida) · field · full text read

    Zhang et al. 2022

Moon

  • Tagged swordfish sat deeper at night near the full moon than near the new moon: a depth note for night baits, not a bite forecast.

    Pop-up satellite tags on 7 swordfish over 3 lunar cycles in 2002. Night depths averaged 77 m with the moon 90% or more lit and 34 m at 10% or less (correlation -0.66 on nightly means). Fish held 0-160 m at night and 350-770 m by day. Very small sample.

    western North Atlantic · field · full text re-read Oct 16, 2026

    Loefer et al. 2007

Light

  • Predators take small fish about twice as often at night as by day, and most often right at the mangrove edge.

    234 one-hour tethering runs with 10-17 cm pinfish at 10, 50 and 110 m from a Biscayne Bay mangrove edge, July-September 2008. Losses ran from about 10% by day at 110 m to nearly 70% at night at 10 m; night removal was about double. Gray snapper, barracuda and juvenile lemon sharks were among identified predators.

    Biscayne Bay · experiment · full text read

    Hammerschlag et al. 2010

Catch and release

  • Most Florida reef anglers know floaters; most help with venting tools, while descending devices see far less use.

    Email survey of 2013 saltwater license holders, 825 completed of 50,000 sent (1.65%). Almost two-thirds of trips were deeper than 30 feet. Nearly three-fourths of deep-water anglers had seen fish struggle to return. Of the 92% using venting tools, about 63% wanted training; descending gear use was much lower. Low response rate.

    Florida statewide · survey · agency document

    Adams et al. 2017
  • Released gray triggerfish die more often when caught in deeper water or when surface water is hot, worst in August.

    Tag returns from 3,744 triggerfish released from for-hire boats off the Florida Panhandle, 2022 to 2024 (depth 20 to 67 m, SST 15 to 31 C). Survival dropped beyond 31.25 m and 22.85 C. At 30 C, modeled mortality was 0.51 at 20 m and 0.96 at 70 m. Monthly mortality ranged 0.06 in February to 0.65 in August.

    Florida Panhandle, eastern Gulf · field · full text read

    Hyman et al. 2026
  • About one in four released mutton snapper on for-hire trips shows impairment or deep hooking; deeper SE Florida fish are vented more.

    For-hire observer data: 44% released in good condition without venting, 26% vented and swam down, 1% descended, 19% impaired, 9% deep-hooked, 1% dead or eaten. Keys fish (shallow) mostly released without barotrauma help; SE Florida fish (deeper) vented far more often.

    Florida Keys; SE Florida · agency · agency document

    Lazarre 2023
  • Updated RECOVER envelope for the St. Lucie: optimum flows top out near 1,400 cfs; stress begins there and damage above 1,700 cfs.

    Martin County comments on the draft 2020 RECOVER Northern Estuaries salinity envelope report a St. Lucie optimum envelope from 150 to 1,400 cfs, stress from 1,400 cfs and damaging flows from 1,700 cfs (14-day averages), replacing the 2007 measure of 350-2,000 cfs.

    St. Lucie Estuary, SE Florida · agency · agency document

    Martin County Board of County Commissioners 2020
  • Caloosahatchee estuary health is best when S-79 flows mostly sit at 450-800 cfs; months above 2,800 cfs push freshwater toward Shell Point.

    CERP RECOVER performance measure (revised 2007): about 75% of S-79 flows should be 450-800 cfs and the rest 800-2,800 cfs. Mean monthly flows over 2,800 cfs make more than half the estuary above Shell Point fresh; over 4,500 cfs degrade San Carlos Bay. Adult oysters die below 3 ppt, reached when S-79 exceeds 4,000 cfs.

    Caloosahatchee Estuary, SW Florida · agency · agency document

    RECOVER 2007
  • C-51 canal pulses of 1,000 cfs or more freshen central Lake Worth Lagoon below the 15 ppt minimum target.

    RECOVER targets for Lake Worth Lagoon: keep C-51 inflow at 0-500 cfs (7-day moving average), eliminate events of 1,000 cfs or more (2-day moving average) and sustained flows over 500 cfs. Minimum desirable salinity is 15 ppt; seagrass target 20 ppt; Halophila died within 3 days at 5 ppt.

    Lake Worth Lagoon (C-51), Palm Beach County · agency · agency document

    RECOVER 2007
  • St. Lucie discharges above about 2,000 cfs drive mid-estuary salinity near 3 ppt, a level that kills oysters and seagrass.

    RECOVER salinity envelope: St. Lucie flows of 725-3,280 cfs produced salinities of 1-5 ppt; 2,000 cfs yields about 3 ppt at mid-estuary, implicated in 1998-1999 oyster deaths. Spring 1998 and summer 1999 releases above 2,000 cfs drove salinity below 1 ppt and killed over 90% of remaining oysters. Target at Roosevelt Bridge is 12-20 ppt.

    St. Lucie Estuary, SE Florida · agency · agency document

    RECOVER 2007
  • Current RECOVER envelope: S-79 at 750-2,100 cfs (14-day average) is optimum; above 2,600 cfs is damaging.

    SCCF weekly condition reports apply the RECOVER 2020 envelope to the S-79 14-day moving average: optimum 750-2,100 cfs, damaging above 2,600 cfs. Example: October 2025, 14-day mean 1,059 cfs, optimum for 11 days after 36 days damaging. The original RECOVER 2020 document was not retrieved here.

    Caloosahatchee Estuary, SW Florida · agency · agency document

    Sanibel-Captiva Conservation Foundation 2025

Other

  • Anglers with cuts should stay out of warm salt or brackish water; Vibrio vulnificus wound infections kill about one in five.

    CDC HAN 00497 (Sept 1, 2023): about 150-200 V. vulnificus infections reported yearly; about 1 in 5 die, some within 1-2 days. Bacteria favor warm, lower-salinity water such as estuaries, May-October. Main route is open wounds in salt or brackish water; floods and storm surge raise exposure, as seen in Florida after Hurricane Ian.

    United States coastal (Florida cited after Hurricane Ian) · agency · agency document

    Centers for Disease Control and Prevention 2023
  • Open coastal waters have satellite chlorophyll limits, mostly 0.2 to 6 ug/L, judged from remote sensing only.

    FDEP coastal nutrient regions use chlorophyll a criteria assessed as annual geometric means of satellite data, with narrative criteria for TN and TP. In the app box 28 coastal segments (14 Atlantic, 14 Gulf) carry limits from 0.20 to 5.98 ug/L, median 2.4. Example Atlantic segments: 1.01 and 0.26 ug/L.

    Atlantic and Gulf open coast segments (box) · agency · agency document

    Florida Department of Environmental Protection 2016
  • Biscayne Bay has legal nutrient limits by segment; chlorophyll a above 0.2 to 1.7 ug/L yearly means water is degrading.

    Florida rule sets annual geometric mean limits for 9 Biscayne Bay segments, not to be exceeded more than once in 3 years. TP 0.006 to 0.012 mg/L, TN 0.24 to 0.58 mg/L, chlorophyll a 0.2 to 1.7 ug/L. Strictest chlorophyll (0.2) is South Central Mid-Bay and Outer-Bay; loosest (1.7) is Northern North Bay.

    Biscayne Bay · agency · agency document

    Florida Department of Environmental Protection 2016
  • Lee County estuaries use annual-mean chlorophyll limits near 4 to 6.5 ug/L; tidal rivers allow up to about 12.6.

    Criteria (annual arithmetic means unless stated): Pine Island Sound chlorophyll 6.5 ug/L, TN 0.57, TP 0.06 mg/L; San Carlos Bay 3.7 ug/L long-term average; Estero Bay 5.9 ug/L; Matlacha Pass 6.1; Charlotte Harbor proper 6.1; Lower, Middle, Upper Caloosahatchee 5.6, 6.5, 4.2 ug/L long-term averages; Tidal Peace River 12.6.

    Charlotte Harbor, Pine Island Sound, San Carlos Bay, Estero Bay, Caloosahatchee · agency · agency document

    Florida Department of Environmental Protection 2016
  • Florida Bay limits vary by basin: open-bay chlorophyll a targets run from 0.4 ug/L (east central) to 2.2 ug/L (central).

    Six Florida Bay segments have annual geometric mean limits: TP 0.007 to 0.045 mg/L, TN 0.37 to 1.29 mg/L, chlorophyll a 0.4 to 9.3 ug/L. East Central is strictest (chl 0.4, TP 0.007); Central 2.2 ug/L; Coastal Lakes loosest (9.3 ug/L, TN 1.29).

    Florida Bay · agency · agency document

    Florida Department of Environmental Protection 2016
  • Florida Keys waters are held to very low nutrient limits; yearly chlorophyll a above about 0.3 ug/L breaks most segment limits.

    Seven Florida Keys segments carry annual geometric mean limits (exceed no more than once in 3 years): TP 0.007 to 0.011 mg/L, TN 0.17 to 0.25 mg/L, chlorophyll a 0.2 to 0.7 ug/L. Upper Keys is strictest for chlorophyll (0.2); Backshelf loosest (0.7).

    Florida Keys · agency · agency document

    Florida Department of Environmental Protection 2016
  • East coast lagoons have looser limits than Biscayne: chlorophyll a targets 1.8 to 10.2 ug/L by segment.

    Lake Worth Lagoon: chlorophyll a 2.9 (north), 10.2 (central), 5.7 (south) ug/L with TN 0.54 to 0.66 mg/L. Loxahatchee: 1.8 (lower) to 5.5 ug/L. St. Lucie Estuary chlorophyll 5.9 ug/L AGM, forks 5.0 to 7.4, TN 0.72 mg/L from the TMDL rule. IRL Hobe Sound reach 2.0 ug/L; St. Lucie to Ft. Pierce 4.7 ug/L.

    Lake Worth Lagoon, Loxahatchee, St. Lucie, southern Indian River Lagoon · agency · agency document

    Florida Department of Environmental Protection 2016
  • SW Florida coastal limits rise from 1.0 ug/L chlorophyll on the outer shelf to about 5 to 6 ug/L in tidal rivers.

    Fifteen segments from the Cocohatchee River to Whitewater Bay carry annual geometric mean limits. Chlorophyll a: Outer Gulf Shelf 1.0, Middle 1.4, Inner 1.6, Shark River Mouth 2.2, Collier Inshore 3.1, Naples Bay 4.3, Rookery Bay/Marco 4.9, Inner Waterway 5.2, Tidal Cocohatchee 5.8 ug/L. TN up to 0.82 mg/L (Whitewater Bay).

    SW Florida: Naples, Rookery Bay, Ten Thousand Islands, Whitewater Bay, Gulf shelf · agency · agency document

    Florida Department of Environmental Protection 2016
  • Florida issues a beach advisory when enterococci exceed 70 per 100 mL on a sample and its resample.

    Florida Healthy Beaches Program rates marine enterococci per 100 mL: good 0-35, moderate 36-70, poor 71 or more. An advisory is issued when the initial sample and a resample both exceed 70 CFU per 100 mL. Stormwater runoff is listed among fecal sources; sampling is roughly every two weeks.

    Florida statewide beaches · agency · agency document

    Florida Department of Health

Out-of-region studies say so beside their region. A study from elsewhere fills a reason in the app only when no South Florida study covers the same fish and factor.

Read in the abstract only

  • Arriola et al. 2025, Ecosystem metabolic rates estimated from diel oxygen measurements in two subtropical estuaries. Water temperature; abstract read, numbers withheld.
  • Ball et al. 2009, Comparison of random forest, artificial neural network, and multi-linear regression: a water temperature prediction case (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Binder et al. 2024, Time-series models and biotelemetry identify behavioral dynamics within a spawning aggregation of a large marine predator. Water temperature; abstract read, numbers withheld.
  • Boucek & Rehage 2014, Climate extremes drive changes in functional community structure. Water temperature; abstract read, numbers withheld.
  • Boucek et al. 2017, Can animal habitat use patterns influence their vulnerability to extreme climate events? An estuarine sportfish case study. Water temperature; abstract read, numbers withheld.
  • Brodie et al. 2015, Modelling the oceanic habitats of two pelagic species using recreational fisheries data (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Brodie et al. 2017, Seasonal forecasting of dolphinfish distribution in eastern Australia to aid recreational fishers and managers (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Brownscombe et al. 2017, Spatiotemporal drivers of energy expenditure in a coastal marine fish (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Dale et al. 2022, Global habitat loss of a highly migratory predator, the blue marlin (Makaira nigricans) (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Ding et al. 2018, Skillful climate forecasts of the tropical Indo-Pacific Ocean using model-analogs (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Duffing Romero et al. 2021, Movement patterns of juvenile Atlantic tarpon (Megalops atlanticus) in Brewers Bay, St. Thomas, U.S. Virgin Islands (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Goodyear 2003, Spatio-temporal distribution of longline catch per unit effort, sea surface temperature and Atlantic marlin. Water temperature; abstract read, numbers withheld.
  • Herbig & Szedlmayer 2016, Movement patterns of gray triggerfish, Balistes capriscus, around artificial reefs in the northern Gulf of Mexico (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Hobday et al. 2011, Seasonal forecasting of tuna habitat for dynamic spatial management (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Hobday et al. 2016, Seasonal forecasting for decision support in marine fisheries and aquaculture (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Hobday et al. 2016, A hierarchical approach to defining marine heatwaves (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Howell et al. 2008, TurtleWatch: a tool to aid in the bycatch reduction of loggerhead turtles Caretta caretta in the Hawaii-based pelagic longline fishery (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Humston et al. 2005, Movements and site fidelity of the bonefish Albula vulpes in the northern Florida Keys determined by acoustic telemetry. Water temperature; abstract read, numbers withheld.
  • Jacox et al. 2022, Global seasonal forecasts of marine heatwaves (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Kaplan et al. 2016, Cloudy with a chance of sardines: forecasting sardine distributions using regional climate models (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Kendall et al. 2022, Too Much Freshwater, Not Enough, or Just Right? Long-Term Trawl Monitoring Demonstrates the Impact of Canals that Altered Freshwater Flow to Three Bays in SW Florida. Water temperature; abstract read, numbers withheld.
  • Kleisner et al. 2006, Towards an understanding of dolphinfish abundance: an interpretation of the relationships between environmental variables and species associations from the US pelagic longline fleet (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Mace et al. 2017, Low-temperature tolerance of juvenile tarpon Megalops atlanticus (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Manzello et al. 2025, Heat-driven functional extinction of Caribbean Acropora corals from Florida's Coral Reef. Water temperature; abstract read, numbers withheld.
  • Nowell et al. 2015, Swimming energetics and thermal ecology of adult bonefish (Albula vulpes): a combined laboratory and field study in Eleuthera, The Bahamas (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Perez et al. 2019, Influence of environmental variables on abundance and movement of bonefish (Albula vulpes) in the Caribbean Sea and a tropical estuary of Belize and Mexico (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Procarione & King 1993, Upper and lower temperature tolerance limits for juvenile red drums from Texas and South Carolina (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Samson et al. 2014, Behavioural and reflex responses of mottled mojarra Eucinostomus lefroyi (Gerreidae) to cold shock exposure (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Santos et al. 2016, Shift in recreational fishing catches as a function of an extreme cold event. Water temperature; abstract read, numbers withheld.
  • Schlegel et al. 2019, Detecting marine heatwaves with sub-optimal data (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Shafland & Foote 1983, A lower lethal temperature for fingerling snook, Centropomus undecimalis. Water temperature; abstract read, numbers withheld.
  • Shi et al. 2024, Temperature Response of South Florida Estuaries to the 2023 Heatwave. Water temperature; abstract read, numbers withheld.
  • Shultz et al. 2016, Thermal tolerance of nearshore fishes across seasons: implications for coastal fish communities in a changing climate (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Silverio et al. 2025, Assessing the resistance and resilience of recreationally important fish species to extreme events in coastal Texas (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Spencer et al. 2026, Thermal performance and activation energy explain flexible thermal habitat use in great hammerhead sharks. Water temperature; abstract read, numbers withheld.
  • Spillman & Hobday 2014, Dynamical seasonal ocean forecasts to aid salmon farm management in a climate hotspot (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Stevens et al. 2016, Resilience of a tropical sport fish population to a severe cold event varies across five estuaries in southern Florida. Water temperature; abstract read, numbers withheld.
  • Stock et al. 2015, Seasonal sea surface temperature anomaly prediction for coastal ecosystems (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Turner et al. 2017, Cooperative research to evaluate an incidental catch distribution forecast (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Ward et al. 1993, Comparisons of critical thermal maxima and minima of juvenile red drum (Sciaenops ocellatus) from Texas and North Carolina (outside South Florida). Water temperature; abstract read, numbers withheld.
  • Boucek & Rehage 2013, No free lunch: displaced marsh consumers regulate a prey subsidy to an estuarine consumer. Season; abstract read, numbers withheld.
  • Epstein 1991, On obtaining daily climatological values from monthly means. Season; abstract read, numbers withheld.
  • Farmer et al. 2020, Forecasting for recreational fisheries management: a derby fishery case study with Gulf of Mexico Red Snapper (outside South Florida). Season; abstract read, numbers withheld.
  • Griffin et al. 2018, Keeping up with the Silver King: Using cooperative acoustic telemetry networks to quantify the movements of Atlantic tarpon (Megalops atlanticus) in the coastal waters of the southeastern United States. Season; abstract read, numbers withheld.
  • Hutchinson et al. 2024, Relationships between postlarval settlement and commercial landings of Caribbean spiny lobster (Panulirus argus) in Florida (USA). Season; abstract read, numbers withheld.
  • Olson et al. 2024, Recruitment of Juvenile Snapper (Lutjanidae) in the Middle Florida Keys: Temporal Trends and Fine-Scale Habitat Associations. Season; abstract read, numbers withheld.
  • Oxenford 1999, Biology of the dolphinfish (Coryphaena hippurus) in the western central Atlantic: a review. Season; abstract read, numbers withheld.
  • Oxenford et al. 2003, The biology of wahoo (Acanthocybium solandri) in the western central Atlantic (outside South Florida). Season; abstract read, numbers withheld.
  • Peters & Nelson 1987, The Seasonality and Spatial Patterns of Juvenile Surf Zone Fishes of the Florida East Coast. Season; abstract read, numbers withheld.
  • Peterson & Grubbs 2023, Temporal community structure and seasonal climatic migration of coastal sharks and large teleost fishes in the northeast Gulf of Mexico (outside South Florida). Season; abstract read, numbers withheld.
  • Rehage & Loftus 2007, Seasonal fish community variation in headwater mangrove creeks in the southwestern Everglades: an examination of their role as dry-down refuges. Season; abstract read, numbers withheld.
  • Rider et al. 2021, Multi-year movements of adult and subadult bull sharks (Carcharhinus leucas): philopatry, connectivity, and environmental influences. Season; abstract read, numbers withheld.
  • Vaudo et al. 2017, Long-term satellite tracking reveals region-specific movements of a large pelagic predator, the shortfin mako shark, in the western North Atlantic Ocean (outside South Florida). Season; abstract read, numbers withheld.
  • Walker et al. 2002, Fish assemblages associated with artificial reefs of concrete aggregates or quarry stone offshore Miami Beach, Florida, USA. Season; abstract read, numbers withheld.
  • Williams et al. 2023, How Are Man-Made Changes in Freshwater Flow Related to the Abundance of Juvenile Estuarine Fishes?. Season; abstract read, numbers withheld.
  • Beardsley 1967, Age, growth, and reproduction of the dolphin, Coryphaena hippurus, in the Straits of Florida. Spawning; abstract read, numbers withheld.
  • Brownscombe et al. 2020, Seasonal occupancy and connectivity amongst nearshore flats and reef habitats by permit Trachinotus falcatus: considerations for fisheries management. Spawning; abstract read, numbers withheld.
  • Brownscombe et al. 2020, Application of machine learning algorithms to identify cryptic reproductive habitats using diverse information sources. Spawning; abstract read, numbers withheld.
  • Bryan et al. 2015. Spawning; abstract read, numbers withheld.
  • Clementi et al. 2026, Permit (Trachinotus falcatus) aggregation fishery dynamics and depredation in the Florida Keys. Spawning; abstract read, numbers withheld.
  • Coleman et al. 1996, Reproductive styles of shallow-water groupers (Pisces: Serranidae) in the eastern Gulf of Mexico and the consequences of fishing spawning aggregations (outside South Florida). Spawning; abstract read, numbers withheld.
  • Coleman et al. 2011, Groupers on the Edge: Shelf Edge Spawning Habitat in and Around Marine Reserves of the Northeastern Gulf of Mexico (outside South Florida). Spawning; abstract read, numbers withheld.
  • Cornic & Rooker 2021, Temporal shifts in the abundance and preferred habitats of yellowfin and bigeye tuna larvae in the Gulf of Mexico (outside South Florida). Spawning; abstract read, numbers withheld.
  • Danylchuk et al. 2011, Aggregations and offshore movements as indicators of spawning activity of bonefish (Albula vulpes) in The Bahamas (outside South Florida). Spawning; abstract read, numbers withheld.
  • Danylchuk et al. 2018, Behavioral observations of bonefish (Albula vulpes) during prespawning aggregations in the Bahamas: clues to identifying spawning sites that can drive broader conservation efforts (outside South Florida). Spawning; abstract read, numbers withheld.
  • Ebert et al. 2026. Spawning; abstract read, numbers withheld.
  • Ellis et al. 2023, Spawning Migrations of the Atlantic Goliath Grouper along the Florida Atlantic Coast. Spawning; abstract read, numbers withheld.
  • Jenkins & McBride 2009, Reproductive biology of wahoo, Acanthocybium solandri, from the Atlantic coast of Florida and the Bahamas (outside South Florida). Spawning; abstract read, numbers withheld.
  • Keller et al. 2020. Spawning; abstract read, numbers withheld.
  • Kitchens & Rooker 2014, Habitat associations of dolphinfish larvae in the Gulf of Mexico (outside South Florida). Spawning; abstract read, numbers withheld.
  • Lombardo et al. 2020, Novel deep-water spawning patterns of bonefish (Albula vulpes), a shallow water fish (outside South Florida). Spawning; abstract read, numbers withheld.
  • Lowerre-Barbieri et al. 2008, Use of Passive Acoustics to Determine Red Drum Spawning in Georgia Waters (outside South Florida). Spawning; abstract read, numbers withheld.
  • Lowerre-Barbieri et al. 2016, Assessing reproductive behavior important to fisheries management: a case study with red drum, Sciaenops ocellatus. Spawning; abstract read, numbers withheld.
  • Reyier et al. 2010, Movement patterns of adult red drum, Sciaenops ocellatus, in shallow Florida lagoons as inferred through autonomous acoustic telemetry. Spawning; abstract read, numbers withheld.
  • Trejo-Martínez J, Brulé T, Morales-López N, Colás-Marrufo T, Sánchez-Crespo M 2021, Reproductive Strategy of a Continental Shelf Lane Snapper Population from the Southern Gulf of Mexico (outside South Florida). Spawning; abstract read, numbers withheld.
  • Trotter et al. 2012, Migrations of Common Snook from a Tidal River with Implications for Skipped Spawning. Spawning; abstract read, numbers withheld.
  • Walters et al. 2009, Using a Passive Acoustic Survey to Identify Spotted Seatrout Spawning Sites and Associated Habitat in Tampa Bay, Florida. Spawning; abstract read, numbers withheld.
  • Young et al. 2016, Spawning Site Fidelity, Catchment, and Dispersal of Common Snook along the East Coast of Florida. Spawning; abstract read, numbers withheld.
  • Adams & Blewett 2004, Spatial patterns of estuarine habitat type use and temporal patterns in abundance of juvenile permit, Trachinotus falcatus, in Charlotte Harbor, Florida. Habitat; abstract read, numbers withheld.
  • Adams et al. 2006, Patterns of Juvenile Habitat Use and Seasonality of Settlement by Permit, Trachinotus falcatus (outside South Florida). Habitat; abstract read, numbers withheld.
  • Arena et al. 2007, Fish assemblages on sunken vessels and natural reefs in southeast Florida, USA. Habitat; abstract read, numbers withheld.
  • Bacheler et al. 2022, Reef fish community structure along the southeastern US Atlantic continental shelf break and upper slope appears resistant to increasing lionfish (Pterois volitans/miles) density. Habitat; abstract read, numbers withheld.
  • Bacheler et al. 2025, Spatiotemporal dynamics and habitat use of red snapper (Lutjanus campechanus) on the southeastern United States Atlantic continental shelf. Habitat; abstract read, numbers withheld.
  • Baron et al. 2004, Characterization of the marine fish assemblage associated with the nearshore hardbottom of Broward County, Florida, USA. Habitat; abstract read, numbers withheld.
  • Bohnsack 2011, Impacts of Florida Coastal Protected Areas on Recreational World Records for Spotted Seatrout, Red Drum, Black Drum, and Common Snook. Habitat; abstract read, numbers withheld.
  • Bryan et al. 2013, Characterization of the mesophotic reef fish community in south Florida, USA. Habitat; abstract read, numbers withheld.
  • Chiappone et al. 2000, Groupers (Pisces: Serranidae) in fished and protected areas of the Florida Keys, Bahamas and northern Caribbean. Habitat; abstract read, numbers withheld.
  • Cianciotto et al. 2019, Modifying mosquito impoundment management to enhance nursery habitat value for juvenile common Snook (Centropomus undecimalis) and Atlantic tarpon (Megalops atlanticus). Habitat; abstract read, numbers withheld.
  • Farmer & Ault 2011, Grouper and snapper movements and habitat use in Dry Tortugas, Florida. Habitat; abstract read, numbers withheld.
  • Farmer & Ault 2014, Modeling coral reef fish home range movements in Dry Tortugas, Florida. Habitat; abstract read, numbers withheld.
  • Fourqurean et al. 2003, Forecasting responses of seagrass distributions to changing water quality using monitoring data. Habitat; abstract read, numbers withheld.
  • Graham et al. 2016, Use of marine protected areas and exclusive economic zones in the subtropical western North Atlantic Ocean by large highly mobile sharks (outside South Florida). Habitat; abstract read, numbers withheld.
  • Hammerschlag & Serafy 2010, Nocturnal fish utilization of a subtropical mangrove-seagrass ecotone. Habitat; abstract read, numbers withheld.
  • Hepner et al. 2018, Patterns and Drivers of Reef Fish Biodiversity in the Florida Keys National Marine Sanctuary from 1999 - 2016. Habitat; abstract read, numbers withheld.
  • Huntington et al. 2017, Facilitation in Caribbean coral reefs: high densities of staghorn coral foster greater coral condition and reef fish composition. Habitat; abstract read, numbers withheld.
  • Kellison et al. 2012, Coral reef fish assemblage shifts and declines in Biscayne National Park, Florida, USA. Habitat; abstract read, numbers withheld.
  • Koenig et al. 2011, Pattern of Recovery of the Goliath Grouper Epinephelus itajara Population in the Southeastern US. Habitat; abstract read, numbers withheld.
  • Kurth et al. 2019, Atlantic Tarpon (Megalops atlanticus) exhibit upper estuarine habitat dependence followed by foraging system fidelity after ontogenetic habitat shifts (outside South Florida). Habitat; abstract read, numbers withheld.
  • Larkin et al. 2010, A mail survey to estimate the fishery dynamics of southern Florida's bonefish charter fleet. Habitat; abstract read, numbers withheld.
  • Martin et al. 2019, Blacktip shark Carcharhinus limbatus presence at fishing piers in South Carolina: association and environmental drivers (outside South Florida). Habitat; abstract read, numbers withheld.
  • Matheson et al. 1999, Changes in seagrass-associated fish and crustacean communities on Florida Bay mud banks: the effects of recent ecosystem changes?. Habitat; abstract read, numbers withheld.
  • Morris et al. 2022, Seagrass in a changing estuary, the Indian River Lagoon, Florida, United States. Habitat; abstract read, numbers withheld.
  • Noonan et al. 2021, Reef Fish Associations with Natural and Artificial Structures in the Florida Keys. Habitat; abstract read, numbers withheld.
  • Nova Southeastern University student symposium 2026, Marine Biodiversity Monitoring and Community Engagement on the Boulder Reefs of Peanut Island. Habitat; abstract read, numbers withheld.
  • O'Brien et al. 2024, Niche structure and habitat shifts for coastal sharks of the US Southeast Atlantic and Gulf of Mexico (outside South Florida). Habitat; abstract read, numbers withheld.
  • Pabon Quintero et al. 2025, Seagrass Non-cryptic Fish Community Structure Across the Florida Keys National Marine Sanctuary-USA: Implications for Biodiversity Monitoring and Conservation. Habitat; abstract read, numbers withheld.
  • Paxton et al. 2020, Meta-Analysis Reveals Artificial Reefs Can Be Effective Tools for Fish Community Enhancement but Are Not One-Size-Fits-All (outside South Florida). Habitat; abstract read, numbers withheld.
  • Pereira et al. 2016, Difference in the trophic structure of fish communities between artificial and natural habitats in a tropical estuary (outside South Florida). Habitat; abstract read, numbers withheld.
  • Peters et al. 2015, Comparison of fish assemblages in restored and natural mangrove habitats along an urban shoreline. Habitat; abstract read, numbers withheld.
  • Piczak et al. 2023, Permit (Trachinotus falcatus) fishing quality and conservation threats in the Florida Keys: a recreational angler and fishing guide survey. Habitat; abstract read, numbers withheld.
  • Rodemann et al. 2023, Residency and Fine-scale Habitat Use of Juvenile Goliath Grouper (Epinephelus Itajara) in a Mangrove Nursery. Habitat; abstract read, numbers withheld.
  • Schloesser et al. 2025, Best practices for common snook stock enhancement identified through iterative release experiments. Habitat; abstract read, numbers withheld.
  • Schopmeyer & Lirman 2015, Occupation dynamics and impacts of damselfish territoriality on recovering populations of the threatened staghorn coral, Acropora cervicornis. Habitat; abstract read, numbers withheld.
  • Sherman et al. 2002, Artificial reef design: void space, complexity, and attractants. Habitat; abstract read, numbers withheld.
  • Sluka 2001, Influence of habitat on grouper abundance in the Florida Keys, U.S.A.. Habitat; abstract read, numbers withheld.
  • Sogard et al. 1987, Epibenthic fish communities on Florida Bay banks: relations with physical parameters and seagrass cover. Habitat; abstract read, numbers withheld.
  • Thayer et al. 1999, Composition of larval, juvenile, and small adult fishes relative to changes in environmental conditions in Florida Bay. Habitat; abstract read, numbers withheld.
  • Trotter et al. 2020, Using Geomorphology to Better Define Habitat Associations of a Large-Bodied Fish, Common Snook Centropomus undecimalis, in Coastal Rivers of Florida. Habitat; abstract read, numbers withheld.
  • Walker et al. 2009, Relationship of reef fish assemblages and topographic complexity on southeastern Florida coral reef habitats. Habitat; abstract read, numbers withheld.
  • Wilson et al. 2019, Atlantic tarpon (Megalops atlanticus) nursery habitats: evaluation of habitat quality and broad-scale habitat identification. Habitat; abstract read, numbers withheld.
  • Winner et al. 2010, Relative Abundance and Distribution of Common Snook along Shoreline Habitats of Florida Estuaries. Habitat; abstract read, numbers withheld.
  • Andrzejaczek et al. 2023, Seasonal and diel habitat use of blue marlin Makaira nigricans in the North Atlantic Ocean. Depth; abstract read, numbers withheld.
  • Arena et al. 2004, Presence of Juvenile Blackfin Snapper, Lutjanus buccanella, and Snowy Grouper, Epinephelus niveatus, on Shallow-water Artificial Reefs. Depth; abstract read, numbers withheld.
  • Bacheler & Ballenger 2018, Decadal-scale decline of scamp (Mycteroperca phenax) abundance along the southeast United States Atlantic coast. Depth; abstract read, numbers withheld.
  • Brodie et al. 2022, Development of Survey Methods to Effectively Sample Juvenile Red Snapper along the Atlantic Coast of Florida. Depth; abstract read, numbers withheld.
  • Bubley et al. 2020, Incorporating depth into habitat use descriptions for sailfish Istiophorus platypterus and habitat overlap with other billfishes in the western North Atlantic (outside South Florida). Depth; abstract read, numbers withheld.
  • Collins & McBride 2015, Variations in reproductive potential between nearshore and offshore spawning contingents of hogfish in the eastern Gulf of Mexico. Depth; abstract read, numbers withheld.
  • Ferro et al. 2005, The Marine Fishes of Broward County, Florida: Final Report of 1998-2002 Survey Results. Depth; abstract read, numbers withheld.
  • Hansen & Kerstetter 2015, Habitat utilization and vertical distribution of the Great Barracuda Sphyraena barracuda (Edwards 1771) in the western North Atlantic using electronic archival tags. Depth; abstract read, numbers withheld.
  • Hoolihan et al. 2014, Vertical and Horizontal Movements of Yellowfin Tuna in the Gulf of Mexico (outside South Florida). Depth; abstract read, numbers withheld.
  • Hoolihan et al. 2015, Vertical and horizontal habitat use by white marlin Kajikia albida (Poey, 1860) in the western North Atlantic Ocean (outside South Florida). Depth; abstract read, numbers withheld.
  • Horodysky et al. 2007, Habitat utilization and vertical movements of white marlin (Tetrapturus albidus) released from commercial and recreational fishing gears in the western North Atlantic Ocean: inferences from short duration pop-up archival satellite tags. Depth; abstract read, numbers withheld.
  • Klibansky et al. 2024, Community structure and environmental drivers of offshore hard-bottom reef fishes in the northern Gulf of Mexico (outside South Florida). Depth; abstract read, numbers withheld.
  • Kraus & Rooker 2007, Patterns of Vertical Habitat Use by Atlantic Blue Marlin (Makaira nigricans) in the Gulf of Mexico (outside South Florida). Depth; abstract read, numbers withheld.
  • Reed et al. 2005, Deep-water sinkholes and bioherms of South Florida and the Pourtales Terrace: habitat and fauna. Depth; abstract read, numbers withheld.
  • Reed et al. 2006, Habitat and fauna of deep-water Lophelia pertusa coral reefs off the southeastern U.S.: Blake Plateau, Straits of Florida, and Gulf of Mexico. Depth; abstract read, numbers withheld.
  • Streich et al. 2026, Seasonal movements and habitat use of cobia (Rachycentron canadum) in the Gulf of Mexico (outside South Florida). Depth; abstract read, numbers withheld.
  • Ellis & Bell 2008, Tidal influence on a fringing mangrove intertidal fish community as observed by in situ video recording: implications for studies of tidally migrating nekton. Tide; abstract read, numbers withheld.
  • Murchie et al. 2013, Movement patterns of bonefish (Albula vulpes) in tidal creeks and coastal waters of Eleuthera, The Bahamas (outside South Florida). Tide; abstract read, numbers withheld.
  • Smith & Curran 2017, Movement Patterns of Sphyrna tiburo (Bonnethead Shark) in a Shallow Tidal Creek System (outside South Florida). Tide; abstract read, numbers withheld.
  • Abad-Uribarren et al. 2019, Modeling environmental influence on Atlantic bluefin tuna bycatch by Mexican longliners in the Gulf of Mexico (outside South Florida). Current; abstract read, numbers withheld.
  • Archer et al. 2017, The Surface Velocity Structure of the Florida Current in a Jet Coordinate Frame. Current; abstract read, numbers withheld.
  • Arostegui et al. 2022, Anticyclonic eddies aggregate pelagic predators in a subtropical gyre (outside South Florida). Current; abstract read, numbers withheld.
  • Biggs & Muller-Karger 1994, Ship and satellite observations of chlorophyll stocks in interacting cyclone-anticyclone eddy pairs in the western Gulf of Mexico (outside South Florida). Current; abstract read, numbers withheld.
  • Davis et al. 2008, Effects of western boundary current dynamics on the internal wave field of the Southeast Florida shelf. Current; abstract read, numbers withheld.
  • Fiechter & Mooers 2003, Simulation of frontal eddies on the East Florida Shelf. Current; abstract read, numbers withheld.
  • Fratantoni et al. 1998, The influence of Loop Current perturbations on the formation and evolution of Tortugas eddies in the southern Straits of Florida. Current; abstract read, numbers withheld.
  • Gibbs et al. 2026, From lab to ocean: bridging swimming energetics and wild movements to understand red drum (Sciaenops ocellatus) behavior in a tidal estuary. Current; abstract read, numbers withheld.
  • Kourafalou et al. 2017, The Dynamics of Cuba Anticyclones (CubANs) and Interaction With the Loop Current/Florida Current System. Current; abstract read, numbers withheld.
  • Lee et al. 1995, Florida Current meanders and gyre formation in the southern Straits of Florida. Current; abstract read, numbers withheld.
  • Merten et al. 2014, Spatial differentiation of dolphinfish (Coryphaena hippurus) movements relative to the Bahamian archipelago (outside South Florida). Current; abstract read, numbers withheld.
  • Zimmerman & Biggs 1999, Patterns of distribution of sound-scattering zooplankton in warm- and cold-core eddies in the Gulf of Mexico, from a narrowband acoustic Doppler current profiler survey (outside South Florida). Current; abstract read, numbers withheld.
  • Blewett & Stevens 2014, Temperature variability in a subtropical estuary and implications for common snook Centropomus undecimalis, a cold-sensitive fish. Fronts and edges; abstract read, numbers withheld.
  • Ellis et al. 2017, Winter severity influences spotted seatrout mortality in a southeast US estuarine system (outside South Florida). Fronts and edges; abstract read, numbers withheld.
  • Gilmore et al. 1978, Hypothermal mortality in marine fishes of south-central Florida, January, 1977. Fronts and edges; abstract read, numbers withheld.
  • Kourafalou & Kang 2012, Florida Current meandering and evolution of cyclonic eddies along the Florida Keys Reef Tract: Are they interconnected?. Fronts and edges; abstract read, numbers withheld.
  • Matich & Heithaus 2012, Effects of an extreme temperature event on the behavior and age structure of an estuarine top predator, Carcharhinus leucas. Fronts and edges; abstract read, numbers withheld.
  • Matich et al. 2020, Long-term monitoring provides insight into estuarine top predator (Carcharhinus leucas) resilience following an extreme weather event. Fronts and edges; abstract read, numbers withheld.
  • Sponaugle et al. 2005, Florida Current frontal eddies and the settlement of coral reef fishes. Fronts and edges; abstract read, numbers withheld.
  • Fiechter & Mooers 2007, Primary production associated with the Florida Current along the East Florida Shelf: Weekly to seasonal variability from mesoscale-resolution biophysical simulations. Upwelling; abstract read, numbers withheld.
  • Lee et al. 1991, Gulf Stream frontal eddy influence on productivity of the southeast U.S. continental shelf. Upwelling; abstract read, numbers withheld.
  • Leichter et al. 1996, Pulsed delivery of subthermocline water to Conch Reef (Florida Keys) by internal tidal bores. Upwelling; abstract read, numbers withheld.
  • Leichter et al. 2003, Episodic nutrient transport to Florida coral reefs. Upwelling; abstract read, numbers withheld.
  • Leichter et al. 2014, Regional synchrony of temperature variation and internal wave forcing along the Florida Keys reef tract. Upwelling; abstract read, numbers withheld.
  • Smith 1983, Temporal and spatial characteristics of summer upwelling along Florida's Atlantic shelf. Upwelling; abstract read, numbers withheld.
  • Yoder et al. 1981, Role of Gulf Stream frontal eddies in forming phytoplankton patches on the outer southeastern shelf. Upwelling; abstract read, numbers withheld.
  • Hernandez Arana et al. 2017, Severe impacts of brown tides caused by Sargassum spp. on near-shore Caribbean seagrass communities (outside South Florida). Floating weed; abstract read, numbers withheld.
  • Merten et al. 2023, Increase in Dolphinfish (Coryphaena hippurus) Fishing Success Off the North Coast of Puerto Rico during Hurricane Leslie (outside South Florida). Floating weed; abstract read, numbers withheld.
  • Moser et al. 1998, Effects of mat morphology on large Sargassum-associated fishes: observations from a remotely operated vehicle (ROV) and free-floating video camcorders (outside South Florida). Floating weed; abstract read, numbers withheld.
  • Rodriguez-Martinez et al. 2019, Faunal mortality associated with massive beaching and decomposition of pelagic Sargassum (outside South Florida). Floating weed; abstract read, numbers withheld.
  • Rudershausen et al. 2010, Feeding Ecology of Blue Marlins, Dolphinfish, Yellowfin Tuna, and Wahoos from the North Atlantic Ocean and Comparisons with other Oceans (outside South Florida). Floating weed; abstract read, numbers withheld.
  • Siceloff et al. 2025, Wayward youth: how maturity, reproduction and seaweed drive snapper (Lutjanus spp.) habitat shifts (outside South Florida). Floating weed; abstract read, numbers withheld.
  • Wang et al. 2019, The great Atlantic Sargassum belt (outside South Florida). Floating weed; abstract read, numbers withheld.
  • Banks et al. 1991, Age-linked changes in salinity tolerance of larval spotted seatrout (Cynoscion nebulosus, Cuvier) (outside South Florida). Salinity; abstract read, numbers withheld.
  • Bradshaw et al. 2023, Effects of low salinities on growth, fatty acid composition, and transcriptome in Florida pompano (Trachinotus carolinus) at early developmental stages. Salinity; abstract read, numbers withheld.
  • Copatti et al. 2024, Common snook (Centropomus undecimalis) juveniles maintained at high temperature and brackish water improve growth, osmoregulation, and antioxidant responses (outside South Florida). Salinity; abstract read, numbers withheld.
  • Froeschke et al. 2020, Spatio-temporal models of juvenile and adult sheepshead (Archosargus probatocephalus) in Tampa Bay, Florida from 1996 to 2016. Salinity; abstract read, numbers withheld.
  • Langevin 2003, Simulation of Submarine Ground Water Discharge to a Marine Estuary: Biscayne Bay, Florida. Salinity; abstract read, numbers withheld.
  • Ley et al. 1999, Fishes in mangrove prop-root habitats of northeastern Florida Bay: distinct assemblages across an estuarine gradient. Salinity; abstract read, numbers withheld.
  • Lorenz & Serafy 2006, Subtropical wetland fish assemblages and changing salinity regimes: implications for Everglades restoration. Salinity; abstract read, numbers withheld.
  • Lorenz 2014, A review of the effects of altered hydrology and salinity on vertebrate fauna and their habitats in northeastern Florida Bay. Salinity; abstract read, numbers withheld.
  • Marshall et al. 2011, Empirical tools for simulating salinity in the estuaries in Everglades National Park, Florida. Salinity; abstract read, numbers withheld.
  • Matich et al. 2022, Delineation of blacktip shark (Carcharhinus limbatus) nursery habitats in the north-western Gulf of Mexico (outside South Florida). Salinity; abstract read, numbers withheld.
  • McDonald et al. 2015, Effect of salinity on the upper lethal temperature tolerance of early-juvenile red drum (outside South Florida). Salinity; abstract read, numbers withheld.
  • Nuttle et al. 2000, Influence of net freshwater supply on salinity in Florida Bay. Salinity; abstract read, numbers withheld.
  • Qiu & Wan 2013, Time series modeling and prediction of salinity in the Caloosahatchee River Estuary. Salinity; abstract read, numbers withheld.
  • Randa et al. 2004, Effects of temperature and salinity on Vibrio vulnificus population dynamics as assessed by quantitative PCR (outside South Florida). Salinity; abstract read, numbers withheld.
  • Ross et al. 2020, Estuarine forecasts at daily weather to subseasonal time scales (outside South Florida). Salinity; abstract read, numbers withheld.
  • Rubec et al. 2019, Modeling and Mapping to Assess Spatial Distributions and Population Numbers of Fish and Invertebrate Species in the Lower Peace River and Charlotte Harbor, Florida. Salinity; abstract read, numbers withheld.
  • Santos et al. 2019, Linking bonefish (Albula vulpes) populations to nearshore estuarine habitats using an otolith microchemistry approach. Salinity; abstract read, numbers withheld.
  • Serafy et al. 1997, Effects of freshwater canal discharge on fish assemblages in a subtropical bay: field and laboratory observations. Salinity; abstract read, numbers withheld.
  • Serrano et al. 2010, Salinity selection and preference of the grey snapper Lutjanus griseus: field and laboratory observations. Salinity; abstract read, numbers withheld.
  • Serrano et al. 2011, Osmoregulatory capabilities of the gray snapper, Lutjanus griseus: salinity challenges and field observations. Salinity; abstract read, numbers withheld.
  • Shultz et al. 2014, Seasonal blood chemistry response of sub-tropical nearshore fishes to climate change (outside South Florida). Salinity; abstract read, numbers withheld.
  • Stalker et al. 2009, Determining spatial and temporal inputs of freshwater, including submarine groundwater discharge, to a subtropical estuary using geochemical tracers, Biscayne Bay, South Florida. Salinity; abstract read, numbers withheld.
  • Eggenberger et al. 2025, Seascape heterogeneity and predictability drive movement strategy selection in estuarine predators. Dissolved oxygen; abstract read, numbers withheld.
  • Geiger et al. 2000, Air breathing and gill ventilation frequencies in juvenile tarpon, Megalops atlanticus: responses to changes in dissolved oxygen, temperature, hydrogen sulfide, and pH. Dissolved oxygen; abstract read, numbers withheld.
  • Lapointe & Clark 1992, Nutrient inputs from the watershed and coastal eutrophication in the Florida Keys. Dissolved oxygen; abstract read, numbers withheld.
  • Loch et al. 2021, Restored Coastal Habitat Can Reel In Juvenile Sportfish: Population and Community Responses in the Indian River Lagoon, Florida, USA. Dissolved oxygen; abstract read, numbers withheld.
  • Pan et al. 2016, Hypoxia tolerance decreases with body size in red drum Sciaenops ocellatus (outside South Florida). Dissolved oxygen; abstract read, numbers withheld.
  • Peterson & Gilmore 1991, Eco-physiology of juvenile snook Centropomus undecimalis (Bloch): life-history implications. Dissolved oxygen; abstract read, numbers withheld.
  • Prince & Goodyear 2006, Hypoxia-based habitat compression of tropical pelagic fishes (outside South Florida). Dissolved oxygen; abstract read, numbers withheld.
  • Prince et al. 2010, Ocean scale hypoxia-based habitat compression of Atlantic istiophorid billfishes. Dissolved oxygen; abstract read, numbers withheld.
  • Stevens et al. 2006, Short-term effects of a low dissolved oxygen event on estuarine fish assemblages following the passage of hurricane Charley. Dissolved oxygen; abstract read, numbers withheld.
  • Stevens et al. 2024, Characterizing juvenile common snook and tarpon habitat to guide conservation and restoration of coastal wetlands. Dissolved oxygen; abstract read, numbers withheld.
  • Troxell et al. 2024, Near real-time monitoring of the Biscayne Bay Watershed (South Florida, USA) and major tributaries by water quality research buoys. Dissolved oxygen; abstract read, numbers withheld.
  • Turley et al. 2022, Relationships between blooms of Karenia brevis and hypoxia across the West Florida Shelf. Dissolved oxygen; abstract read, numbers withheld.
  • Wannamaker & Rice 2000, Effects of hypoxia on movements and behavior of selected estuarine organisms from the southeastern United States. Dissolved oxygen; abstract read, numbers withheld.
  • Welsh et al. 2026, Oxygen supply capacity across early-life stages in common snook Centropomus undecimalis. Dissolved oxygen; abstract read, numbers withheld.
  • Barnes et al. 2013, MODIS-derived spatiotemporal water clarity patterns in optically shallow Florida Keys waters: a new approach to remove bottom contamination. Water clarity; abstract read, numbers withheld.
  • Benfield & Minello 1996, Relative effects of turbidity and light intensity on reactive distance and feeding of an estuarine fish (outside South Florida). Water clarity; abstract read, numbers withheld.
  • Boyer et al. 1999, Seasonal and long-term trends in the water quality of Florida Bay (1989-1997). Water clarity; abstract read, numbers withheld.
  • Cunning et al. 2019, Extensive coral mortality and critical habitat loss following dredging and their association with remotely-sensed sediment plumes. Water clarity; abstract read, numbers withheld.
  • Kelble et al. 2005, Attenuation of photosynthetically available radiation (PAR) in Florida Bay: potential for light limitation of primary producers. Water clarity; abstract read, numbers withheld.
  • Lunt & Smee 2015, Turbidity interferes with foraging success of visual but not chemosensory predators. Water clarity; abstract read, numbers withheld.
  • Stabenau et al. 2004, Role of the seagrass Thalassia testudinum as a source of chromophoric dissolved organic matter in coastal south Florida. Water clarity; abstract read, numbers withheld.
  • Stumpf et al. 1999, Variations in water clarity and bottom albedo in Florida Bay from 1985 to 1997. Water clarity; abstract read, numbers withheld.
  • Wang et al. 2012, Characterization of turbidity in Florida's Lake Okeechobee and Caloosahatchee and St. Lucie estuaries using MODIS-Aqua measurements. Water clarity; abstract read, numbers withheld.
  • Zepp et al. 2008, Spatial and temporal variability of solar ultraviolet exposure of coral assemblages in the Florida Keys: importance of colored dissolved organic matter. Water clarity; abstract read, numbers withheld.
  • Blewett et al. 2017, Ecological effects of river flooding on abundance and body condition of a large, euryhaline fish. Runoff and freshwater flow; abstract read, numbers withheld.
  • Caccia & Boyer 2005, Spatial patterning of water quality in Biscayne Bay, Florida as a function of land use and water management. Runoff and freshwater flow; abstract read, numbers withheld.
  • Chin 2025, Identifying associations of water quality parameters using cluster analysis: a case study of Biscayne Bay, USA. Runoff and freshwater flow; abstract read, numbers withheld.
  • Corbett et al. 1999, Patterns of groundwater discharge into Florida Bay. Runoff and freshwater flow; abstract read, numbers withheld.
  • Ferro et al. 2005, The Marine Fishes of Broward County, Florida: Final Report of 1998-2002 Survey Results. Runoff and freshwater flow; abstract read, numbers withheld.
  • Futch et al. 2011, Evaluation of sewage source and fate on southeast Florida coastal reefs. Runoff and freshwater flow; abstract read, numbers withheld.
  • Kerfoot et al. 2023, Detecting Trends in Abundance and Distribution of Seagrasses in Lake Worth Lagoon, Palm Beach County, Florida. Runoff and freshwater flow; abstract read, numbers withheld.
  • Lapointe et al. 1990, Nutrient couplings between on-site sewage disposal systems, groundwaters, and nearshore surface waters of the Florida Keys. Runoff and freshwater flow; abstract read, numbers withheld.
  • Lapointe et al. 2019, Nitrogen enrichment, altered stoichiometry, and coral reef decline at Looe Key, Florida Keys, USA: a 3-decade study. Runoff and freshwater flow; abstract read, numbers withheld.
  • Massie et al. 2025, Linking a seasonal freshwater prey subsidy to the body condition of an estuarine consumer in a subtropical coastal river. Runoff and freshwater flow; abstract read, numbers withheld.
  • Santos et al. 2018, Spatial patterns of seagrasses and salinity regimes interact to structure marine faunal assemblages in a subtropical bay. Runoff and freshwater flow; abstract read, numbers withheld.
  • Serafy et al. 1997, Effects of freshwater canal discharge on fish assemblages in a subtropical bay: field and laboratory observations. Runoff and freshwater flow; abstract read, numbers withheld.
  • Swart et al. 2026, The nitrogen isotopic composition of biotic components in Northern Biscayne Bay and associated waterways, South Florida USA: implications for sources of nitrogen. Runoff and freshwater flow; abstract read, numbers withheld.
  • Szmant & Forrester 1996, Water column and sediment nitrogen and phosphorus distribution patterns in the Florida Keys, USA. Runoff and freshwater flow; abstract read, numbers withheld.
  • Valencia et al. 2024, Septic return flow pathlines, endpoints, and flows based on the urban Miami-Dade groundwater model. Runoff and freshwater flow; abstract read, numbers withheld.
  • Whaley et al. 2023, The influence of freshwater inflow and seascape context on occurrence of juvenile spotted seatrout Cynoscion nebulosus across a temperate estuary. Runoff and freshwater flow; abstract read, numbers withheld.
  • Bechard & Lang 2024, The human health effects of harmful algal blooms in Florida: The importance of high resolution data. Red tide and algal blooms; abstract read, numbers withheld.
  • Berens McCabe et al. 2021, Effects of Multiple Karenia brevis Red Tide Blooms on a Common Bottlenose Dolphin (Tursiops truncatus) Prey Fish Assemblage: Patterns of Resistance and Resilience in Sarasota Bay, Florida. Red tide and algal blooms; abstract read, numbers withheld.
  • Briceno & Boyer 2010, Climatic controls on phytoplankton biomass in a sub-tropical estuary, Florida Bay, USA. Red tide and algal blooms; abstract read, numbers withheld.
  • Butler et al. 1995, Cascading disturbances in Florida Bay, USA: cyanobacteria blooms, sponge mortality, and implications for juvenile spiny lobsters Panulirus argus. Red tide and algal blooms; abstract read, numbers withheld.
  • Cloern & Jassby 2025, Chlorophyll trends are negative for lakes but positive for estuarine-coastal waters (outside South Florida). Red tide and algal blooms; abstract read, numbers withheld.
  • Flaherty & Landsberg 2011, Effects of a persistent red tide (Karenia brevis) bloom on community structure and species-specific relative abundance of nekton in a Gulf of Mexico estuary. Red tide and algal blooms; abstract read, numbers withheld.
  • Gannon et al. 2009, Effects of Karenia brevis harmful algal blooms on nearshore fish communities in southwest Florida. Red tide and algal blooms; abstract read, numbers withheld.
  • Getz et al. 2025, Season and red tide influence Common Snook movement and residency in a channelized estuary (outside South Florida). Red tide and algal blooms; abstract read, numbers withheld.
  • Glibert et al. 2004, Evidence for dissolved organic nitrogen and phosphorus uptake during a cyanobacterial bloom in Florida Bay. Red tide and algal blooms; abstract read, numbers withheld.
  • Glibert et al. 2025, More sustained, more severe blooms and shifting monthly patterns of the toxigenic dinoflagellate Karenia brevis on the West Florida Shelf. Red tide and algal blooms; abstract read, numbers withheld.
  • Gray DiLeone & Ainsworth 2019, Effects of Karenia brevis harmful algal blooms on fish community structure on the West Florida Shelf. Red tide and algal blooms; abstract read, numbers withheld.
  • Kirkpatrick et al. 2008, Florida red tide and human health: A pilot beach conditions reporting system to minimize human exposure. Red tide and algal blooms; abstract read, numbers withheld.
  • Kramer et al. 2018, Nitrogen limitation, toxin synthesis potential, and toxicity of cyanobacterial populations in Lake Okeechobee and the St. Lucie River Estuary, Florida, during the 2016 state of emergency event. Red tide and algal blooms; abstract read, numbers withheld.
  • Landsberg et al. 2006, Saxitoxin puffer fish poisoning in the United States, with the first report of Pyrodinium bahamense as the putative toxin source. Red tide and algal blooms; abstract read, numbers withheld.
  • Lopez et al. 2021, High-resolution spatiotemporal dynamics of harmful algae in the Indian River Lagoon (Florida): a case study of Aureoumbra lagunensis, Pyrodinium bahamense, and Pseudo-nitzschia. Red tide and algal blooms; abstract read, numbers withheld.
  • Millette et al. 2019, Using spatial variability in the rate of change of chlorophyll a to improve water quality management in a subtropical oligotrophic estuary. Red tide and algal blooms; abstract read, numbers withheld.
  • Peterson et al. 2006, Potential role of sponge communities in controlling phytoplankton blooms in Florida Bay. Red tide and algal blooms; abstract read, numbers withheld.
  • Phlips et al. 1999, Blooms of the picoplanktonic cyanobacterium Synechococcus in Florida Bay, a subtropical inner-shelf lagoon. Red tide and algal blooms; abstract read, numbers withheld.
  • Phlips et al. 2006, Factors affecting the distribution of Pyrodinium bahamense var. bahamense in coastal waters of Florida. Red tide and algal blooms; abstract read, numbers withheld.
  • Preece et al. 2017, A review of microcystin detections in estuarine and marine waters: environmental implications and human health risk (outside South Florida). Red tide and algal blooms; abstract read, numbers withheld.
  • Ross et al. 2022, Beach-level 24-hour forecasts of Florida red tide-induced respiratory irritation. Red tide and algal blooms; abstract read, numbers withheld.
  • Zhang 2023, Cyanobacteria blooms induced precipitation of calcium carbonate and dissolution of silica in a subtropical lagoon, Florida Bay, USA. Red tide and algal blooms; abstract read, numbers withheld.
  • Massie et al. 2022, Primed and cued: long-term acoustic telemetry links interannual and seasonal variations in freshwater flows to the spawning migrations of Common Snook in the Florida Everglades. Rain; abstract read, numbers withheld.
  • Payne et al. 2013, Rain reverses diel activity rhythms in an estuarine teleost (outside South Florida). Rain; abstract read, numbers withheld.
  • Santos et al. 2025, Cause and consequences of common snook (Centropomus undecimalis) space use specialization in a subtropical riverscape. Rain; abstract read, numbers withheld.
  • Werry et al. 2018, Rainfall and sea surface temperature: key drivers for occurrence of bull shark, Carcharhinus leucas, in beach areas (outside South Florida). Rain; abstract read, numbers withheld.
  • Junk et al. 2015, Analog-based ensemble model output statistics. Wind; abstract read, numbers withheld.
  • Pitts 2002, Tidal and wind-driven circulation through Lignum Vitae Basin, Florida Bay. Wind; abstract read, numbers withheld.
  • Appendini et al. 2013, Wave modeling performance in the Gulf of Mexico and Western Caribbean: wind reanalyses assessment (outside South Florida). Sea state; abstract read, numbers withheld.
  • Bacheler et al. 2019, Tropical storms influence the movement behavior of a demersal oceanic fish species (outside South Florida). Sea state; abstract read, numbers withheld.
  • Callihan 2011, Spatial ecology of adult spotted seatrout, Cynoscion nebulosus, in Louisiana coastal waters (outside South Florida). Cold fronts; abstract read, numbers withheld.
  • Kemp et al. 2016, Life after cold death: reef coral and coral reef responses to the 2010 cold water anomaly in the Florida Keys. Cold fronts; abstract read, numbers withheld.
  • Heupel et al. 2003, Running before the storm: blacktip sharks respond to falling barometric pressure associated with Tropical Storm Gabrielle. Barometric pressure; abstract read, numbers withheld.
  • Carver et al. 2025, Reef fish movement and community assemblages associated with a newly deployed artificial reef (outside South Florida). Hurricanes and storms; abstract read, numbers withheld.
  • Chen & Li 2025, Impact of Hurricane Ian (2022) on Karenia brevis Bloom on the West Florida Shelf. Hurricanes and storms; abstract read, numbers withheld.
  • Chen & Li 2026, Discerning drivers of a coastal Karenia brevis bloom after Hurricane Ian (2022) on the West Florida Shelf. Hurricanes and storms; abstract read, numbers withheld.
  • Greenwood et al. 2006, Effects of the 2004 hurricanes on the fish assemblages in two proximate southwest Florida estuaries: change in the context of interannual variability. Hurricanes and storms; abstract read, numbers withheld.
  • Gutowsky et al. 2021, Large sharks exhibit varying behavioral responses to major hurricanes (outside South Florida). Hurricanes and storms; abstract read, numbers withheld.
  • Hong et al. 2026, Karenia brevis on the West Florida Shelf: MODIS Satellite Tracking of Bloom Dynamics Following Hurricanes Helene and Milton. Hurricanes and storms; abstract read, numbers withheld.
  • Locascio & Mann 2005, Effects of Hurricane Charley on fish chorusing. Hurricanes and storms; abstract read, numbers withheld.
  • Massie et al. 2020, Going downriver: patterns and cues in hurricane-driven movements of common snook in a subtropical coastal river. Hurricanes and storms; abstract read, numbers withheld.
  • Midway & Miller 2023, Heat, hurricanes, and health: Effects of natural disturbances on angling effort (outside South Florida). Hurricanes and storms; abstract read, numbers withheld.
  • Paperno et al. 2006, The disruption and recovery of fish communities in the Indian River Lagoon, Florida, following two hurricanes in 2004. Hurricanes and storms; abstract read, numbers withheld.
  • Reustle et al. 2024, Hurricanes temporarily weaken human-ecosystem linkages in estuaries (outside South Florida). Hurricanes and storms; abstract read, numbers withheld.
  • Secor et al. 2019, Ocean destratification and fish evacuation caused by a Mid-Atlantic tropical storm (outside South Florida). Hurricanes and storms; abstract read, numbers withheld.
  • Tillman et al. 2025, Acute Impacts of Hurricane Ian on Benthic Habitats, Water Quality, and Microbial Community Composition on the Southwest Florida Shelf. Hurricanes and storms; abstract read, numbers withheld.
  • Wachnicka et al. 2019, Hurricane Irma's impact on water quality and phytoplankton communities in Biscayne Bay (Florida, USA). Hurricanes and storms; abstract read, numbers withheld.
  • Watterson et al. 1998, Movement of Red Snapper, Lutjanus campechanus, in the North Central Gulf of Mexico: Potential Effects of Hurricanes (outside South Florida). Hurricanes and storms; abstract read, numbers withheld.
  • Debaere et al. 2024, The lunar cycle does not influence catch rates or foraging success of neonatal reef sharks in an amphidromic nursery system (outside South Florida). Moon; abstract read, numbers withheld.
  • Hanson et al. 2008, Effects of lunar cycles on the activity patterns and depth use of a temperate sport fish, the largemouth bass, Micropterus salmoides (outside South Florida). Moon; abstract read, numbers withheld.
  • Heyman et al. 2005, Spawning aggregations of Lutjanus cyanopterus (Cuvier) on the Belize Barrier Reef over a 6 year period (outside South Florida). Moon; abstract read, numbers withheld.
  • Fourqurean & Zieman 1991, Photosynthesis, respiration and whole plant carbon budget of the seagrass Thalassia testudinum. Light; abstract read, numbers withheld.
  • Kenworthy & Fonseca 1996, Light requirements of seagrasses Halodule wrightii and Syringodium filiforme derived from the relationship between diffuse light attenuation and maximum depth distribution. Light; abstract read, numbers withheld.
  • Steward et al. 2005, Setting seagrass depth, coverage, and light targets for the Indian River Lagoon system, Florida. Light; abstract read, numbers withheld.
  • Boyle et al. 2023, Diel patterns of depth use and swimming activity of post-release greater amberjack (Seriola dumerili) in the northern Gulf of Mexico (outside South Florida). Catch and release; abstract read, numbers withheld.
  • Griffin et al. 2022, Predator-prey landscapes of large sharks and game fishes in the Florida Keys. Catch and release; abstract read, numbers withheld.
  • Hyman et al. 2026, Depth and sea surface temperature drive post-release condition of reef-associated fishes. Catch and release; abstract read, numbers withheld.
  • Logan et al. 2022, High-resolution post-release behaviour and recovery periods of two highly prized recreational sportfish: the blue marlin and sailfish (outside South Florida). Catch and release; abstract read, numbers withheld.
  • Medina et al. 2022, Nitrogen-enriched discharges from a highly managed watershed intensify red tide (Karenia brevis) blooms in southwest Florida. Catch and release; abstract read, numbers withheld.
  • Prince et al. 2007, Circle hooks, 'J' hooks and drop-back time: a hook performance study of the south Florida recreational live-bait fishery for sailfish, Istiophorus platypterus. Catch and release; abstract read, numbers withheld.
  • Rudershausen et al. 2019, Estimating Discard Mortality for Dolphinfish in a Recreational Hook-and-Line Fishery (outside South Florida). Catch and release; abstract read, numbers withheld.
  • Walter et al. 2012, Can Circle Hooks Improve Western Atlantic Sailfish, Istiophorus Platypterus, Populations?. Catch and release; abstract read, numbers withheld.
  • Briceno et al. 2013, Biogeochemical classification of South Florida's estuarine and coastal waters. Other; abstract read, numbers withheld.
  • Castillo et al. 2024, Understanding pharmaceutical exposure and the potential for effects in marine biota: a survey of bonefish (Albula vulpes) across the Caribbean Basin. Other; abstract read, numbers withheld.
  • Castillo et al. 2024, Widespread pharmaceutical exposure at concentrations of concern for a subtropical coastal fishery: bonefish (Albula vulpes). Other; abstract read, numbers withheld.
  • DelSole & Tippett 2016, Forecast comparison based on random walks. Other; abstract read, numbers withheld.
  • Gledhill et al. 2008, Ocean acidification of the Greater Caribbean Region 1996-2006. Other; abstract read, numbers withheld.
  • Hamill & Juras 2006, Measuring forecast skill: is it real skill or is it the varying climatology?. Other; abstract read, numbers withheld.
  • Hamill & Whitaker 2006, Probabilistic quantitative precipitation forecasts based on reforecast analogs: theory and application. Other; abstract read, numbers withheld.
  • Heemsoth et al. 2020, Swordfish Xiphias gladius diet in the Florida Straits. Other; abstract read, numbers withheld.
  • Jacox et al. 2020, Seasonal-to-interannual prediction of North American coastal marine ecosystems: forecast methods, mechanisms of predictability, and priority developments. Other; abstract read, numbers withheld.
  • Keller et al. 2024, The Reef Visual Census: a review of an essential long- term data source for reef-fish management in Florida. Other; abstract read, numbers withheld.
  • Lorenz 1969, Atmospheric predictability as revealed by naturally occurring analogues. Other; abstract read, numbers withheld.
  • Manzello et al. 2012, Ocean acidification refugia of the Florida Reef Tract. Other; abstract read, numbers withheld.
  • McBride et al. 2008, Age, growth, and mortality of wahoo, Acanthocybium solandri, from the Atlantic coast of Florida and the Bahamas (outside South Florida). Other; abstract read, numbers withheld.
  • McClenachan 2009, Documenting Loss of Large Trophy Fish from the Florida Keys with Historical Photographs. Other; abstract read, numbers withheld.
  • Merten et al. 2022, A citizen science approach to enhance dolphinfish (Coryphaena hippurus) data collection to improve species management. Other; abstract read, numbers withheld.
  • Muehllehner et al. 2016, Dynamics of carbonate chemistry, production, and calcification of the Florida Reef Tract (2009-2010): evidence for seasonal dissolution. Other; abstract read, numbers withheld.
  • Murphy 1988, Skill scores based on the mean square error and their relationships to the correlation coefficient. Other; abstract read, numbers withheld.
  • Murphy 1992, Climatology, persistence, and their linear combination as standards of reference in skill scores. Other; abstract read, numbers withheld.
  • Nehemiah et al. 2025, Evaluating fisheries-independent annual recruitment indices for Spotted Seatrout in two Florida estuaries. Other; abstract read, numbers withheld.
  • Ortiz et al. 2003, Global overview of the major constituent-based billfish tagging programs and their results since 1954 (outside South Florida). Other; abstract read, numbers withheld.
  • Payne et al. 2017, Lessons from the first generation of marine ecological forecast products (outside South Florida). Other; abstract read, numbers withheld.
  • Rajagopalan & Lall 1999, A k-nearest-neighbor simulator for daily precipitation and other weather variables. Other; abstract read, numbers withheld.
  • Rehage et al. 2025, A multi-estuary assessment of pharmaceutical exposure and risk of pharmacological effects in a recreational fishery. Other; abstract read, numbers withheld.
  • Richardson 2000, Skill and relative economic value of the ECMWF ensemble prediction system. Other; abstract read, numbers withheld.
  • Runde et al. 2025, Evidence for declining numbers of large Dolphinfish in the western North Atlantic (outside South Florida). Other; abstract read, numbers withheld.
  • van den Dool HM 1989, A new look at weather forecasting through analogues. Other; abstract read, numbers withheld.

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Research cited

Research cited: Bonefish & Tarpon Trust; Beneath the Waves; Dolphinfish Research Program (Beyond Our Shores); FAU Harbor Branch Oceanographic Institute; FIU Florida Coastal Everglades LTER and Coastal Fisheries Lab; FWC FWRI Fisheries-Independent Monitoring (FIM); Florida Sea Grant and Return 'Em Right; Ocean Research & Conservation Association (ORCA). Cited, not endorsed.

The fish pages carry the same studies by species: every fish. The feeds the app reads are on the sources page.

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